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Important Plant Areas of Ukraine Editor: V.A. Onyshchenko Selecion criteria УДК 502.75(477) В12 Aconitum pseudanthora Błocki ex Pacz. LC * * - R Kamiani Mohyly * - - - - * - - - - V Medobory; Kniazhpilskyi Lis; Sovyi Yar; Vasylivskyi i Rozkopynskyi Yary; Shebutynskyi Yar; Ternava – Dnister V Probabyn, Vymushiv * 3 RDBU RBEB © V.A. Onyshchenko (editor), 2017 © M.G. Kholodny Insitute of Botany, 2017 © Alterpress, 2017 Res 6 ISBN 978-966-542-622-6 Achillea glaberrima Klokov Aconitum besserianum Andrz. ex Trautv. BC Reviewers: S.L. Mosyakin, O.M. Bayrak Taxon IUCN db 2015-4 Edited by V.A. Onyshchenko Co-edited (English text and plant names) by S.L. Mosyakin Table 1. Criterion A species and corresponding selected areas. A(iv) Approved by the Academic Council of the M.G. Kholodny Insitute of Botany, Naional Academy of Sciences of Ukraine A(iii) Authors: V.A. Onyshchenko, V.P. Kolomiychuk, I.I. Chorney, R.Ya. Kish, A.I. Tokariuk, V.V. Budzhak, O.O. Orlov, H.I. Oliiar, O.V. Bezrodnova, O.M. Derkach, N.O. Stetsiuk, N.V. Shumska, M.V. Banik, H.V. Kolomiets, L.H. Lubinska, V.V. Datsiuk, M.M. Peregrym, I.M. Danylyk, O.M. Popova, O.T. Kuzyarin, O.V. Holovko, O.I. Pryadko, L.T. Horbnyak, V.A. Kolodiy, L.V. Markivska, O.V. Lukash, N.B. Saidakhmedova, H.P. Protsiv, O.Yu. Umanets, T.D. Solomakha, V.M. Virchenko, V.V. Rasevich A(i) Важливі ботанічні території України / за ред. В.А. Онищенка. – Київ: Альтерпрес, 2017. – 376 с. ISBN 978-966-542-622-6 Книга містить описи 173 Важливих ботанічних територій України. Дані про кожну територію включають її площу, географічні координати, критерії виділення, площі оселищ за класифікацією EUNIS, характеристику рослинності, загрози, види людської діяльності, інформацію про природно-заповідні території, список літератури і карту на основі космічної фотографії. The aim of the Important Plant Areas (IPAs) programme is to idenify and protect a network of the best sites for plant conservaion throughout Europe and the rest of the world, using consistent criteria (Anderson, 2002). The ideniicaion of IPAs is based on three criteria. Criterion A – Presence of threatened plant species: the site holds signiicant populaions of one or more species that are of global or regional conservaion concern. Criterion B – Presence of botanical richness: the site has an excepionally rich lora in a regional context in relaion to its biogeographic zone. Criterion C – Presence of threatened habitats: the site is an outstanding example of a habitat or vegetaion type of global or regional plant conservaion and botanical importance. "IPA" is not an oicial designaion. IPAs are selected scieniically using criteria supported by expert scieniic judgement. IPA criteria were published in 2001 (Palmer & Smart 2001). Since then IPA were selected in many countries. In Ukraine, irst six IPAs were ideniied in 2008 (Onyshchenko et al. 2008). In 2012 16 new areas were selected in the Sea of Azov region (Kolomiychuk et. al. 2012). The present book includes informaion about 173 IPAs ideniied within the territory of Ukraine. These data are available also in the IPA database online. IPAs were ideniied in Ukraine mainly using criteria A and C. Criterion A includes subcriteria A(i) (species with categories EX, CR, En and VU in the IUCN database version 2015–4), A(ii) (species listed in Appendix I of the Bern Convenion, Resoluion 6 of the Steering Commitee of the Bern Convenion, or the Red Data Book of European bryophytes), A(iii) (species with categories "endangered" and "vulnerable" in the Red Data Book of Ukraine (2009) that are considered naional endemics of Ukraine), A(iv) (limited range species with categories "endangered" and "vulnerable" in the Red Data Book of Ukraine (2009) that are not naional endemics). Totally the Criterion A list for Ukraine has 185 species (table 1): subcriterion A(i) – 23 species, A(ii) – 96, A(iii) – 33, and A(iv) – 65 species. 145 species were used as criteria. A(ii) Important Plant Areas of Ukraine / V.A. Onyshchenko (editor). – Kyiv: Alterpress, 2017. – 376 p. The book contains descripions of 173 Important Plant Areas of Ukraine. Data on each site include its area, geographical coordinates, selecion criteria, areas of EUNIS habitat types, characterizaion of vegetaion, threats, human aciviies, informaion about protected areas, references, and a map on the satelite image background. IPAs where the taxon is a criterion of selecion - - - - Byriuchyi Ostriv; Arabatska Strilka; Peresyp Aktaskoho Ozera; Kazantyp - Kozachelaherska Arena; Nyzhniodniprovski Pisky; Biriuchyi Ostriv; Dnipro – Orlil R Zaplava Prypiai; Shatski Ozera; Dunaiski Plavni E Molochnyi Lyman; Kazantyp; Bereh Syvashyka R Molochnyi Lyman; Tendrivska Zatoka; Askania-Nova; Bereh Syvashyka V Nyzhniodniprovski Pisky; Dnipro – Oril; Triokhizbenskyi Step; Volyzhyn Lis V Skhidnyi Churiuk; Tendrivska Zatoka V – * Aldrovanda vesiculosa L. * Allium pervesitum Klokov * * * * Allium savranicum (Nyman) Oxner Allium sphaeropodum Klokov Alyssum borzaeanum Nyár. (Odontarrhena borzaeana (Nyár.) D.A.German) Alyssum gymnopodum P.A.Smirn. (Odontarrhena gymnopoda (P.A.Smirn.) D.A.German) Alyssum savranicum Andrz. ex Besser (Odontarrhena savranica (Andrz. ex Besser) D.A.German) - - - En * * - En - - - - * Allium scythicum Zoz En * * * - * - * - - - DD - - - - - - - - * - - V Peresyp Aktaskoho Ozera; Tendrivska Zatoka * - - - - V Kreidiana Flora; Oskilski Skhyly; Petro-Ivanivka; Marina Hora * - - - - E Nyzhniodniprovski Pisky; Kozachelaherska Arena; Volyzhyn Lis 4 Astragalus setosulus Gontsch. Astragalus tanaiticus C. Koch Astragalus zingeri Korsh. Barbula enderesii Garov. Betula oycoviensis Besser Botrychium matricarifolium A.Br. ex Koch Botrychium muliidum (S.G.Gmel.) Rupr. Brassica taurica (Tzvelev) Tzvelev Buxbaumia viridis (Moug. ex Lam. et DC.) Brid. ex Moug. et Nestl. Caldesia parnassifolia (L.) Parl. Calophaca wolgarica (Moug.) Moug. et Nestl. Campanula abieina Griseb. et Schenk RBEB En - E V Chornohora - - - - * - * * - E Vovchanski Skyly; Oskilski Skhyly; Petro-Ivanivka - – * - - - V V – * - - - - V Krymski Hory; Mehanom; Tepe-Oba; Karadah * - - - - Vu * * - E Ak-Monaiskyi Step; Askania-Nova; Mehanom; Tepe-Oba E Krymski Hory; Mehanom Vu * * - R Kamiani Mohyly * Vu - * - V - E E * - * - - * EN * * - R Chyvchyny; Marmaroski Hory V Ayu-Dah; Mys Marian * - * * V - Chornohora * LC * * - E – LC - - - V Troitska Balka - * - - - Chyvchyny; Marmaroski Hory; Svydovets; Chornohora * Anacamptodon splachnoides (Brid.) Brid. Androsace kosopoljanskii Ovcz. Angelica palustris (Besser) Hofm. Anoectangium handelii Schiffn. Astracantha arnacantha (M.Bieb.) Podlech (Astragalus arnacantha M.Bieb.) Astragalus reduncus Pall. * * * * * * * * * * * * 5 RDBU - – Res 6 - BC * IUCN db 2015-4 - - A(iv) - - A(iii) * Taxon A(i) RBEB - Sinozhai, Dziurkach IPAs where the taxon is a criterion of selecion A(ii) Res 6 - RDBU BC * A(iv) - A(ii) - A(iii) * * Agropyron dasyanthum Ledeb. Allium regelianum A.Becker ex Iljin IUCN db 2015-4 Adenophora lilifolia (L.) Ledeb. Agrimonia pilosa Ledebour Agropyron cimmericum Nevski A(i) Taxon IPAs where the taxon is a criterion of selecion – – – Chyvchyny; Svydovets; Chornohora - - * - - - - * Vu * * - * - - - - * - - - - * - - - - V Kozachelaherska Arena; Nyzhniodniprovski Pisky V Krymski Hory - - - - V Sviai Hory * * - - - - * - - - - E Kurylivka; Kuchuhury E Mykhailo-Laryne; Kovalivka E Mishkovo-Pohorilove * - - - - - - - - E Bobrovyi Kut; Novohredneve E – - - - - E Halitsynove Ex * * - R Kamiani Mohyly Carlina cirsioides Klokov Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł. Centaurea appendicata Klokov Centaurea breviceps Iljin * Centaurea comperiana Steven Centaurea donetzica Klokov Centaurea konkae Klokov Centaurea margaritaalba Klokov Centaurea margaritacea * Ten. Centaurea paczoskii Kotov ex Klokov Centaurea protogerberi Klokov Centaurea protomargaritacea Klokov Centaurea * pseudoleucolepis Kleopow Centaurea sarandinakiae N.B.Illar. Centaurea taliewii Kleopow (Rhaponicoides taliewii (Kleopow) M.V.Agab. & Greuter) * * * * * V Dunaiski Plavni; Nyzhnii Dnipro; Hrakove V Chortova Hora; Kasova Hora; Horodnytski Tovtry V Velyki Holdy; Lysa Hora i Sinka; Vasylivka; Pidlyska Hora E Lysohirka * - - - - V Krymski Hory; Karadah * - - - - V Tarkhankut; Askania-Nova 6 RBEB * - - - E Krymski Hory; Karadah - - - - E – * - - - - * - - - - * - - - - * - - - - V Hranitno-Stepove Pobuzhia V Yelanetskyi Step; Mykhailivskyi Step; Zelena Balka V Kadubivska Sinka; Probabyn; Medobory V Krymski Hory * * En * * - E Kolivska Ulohovyna * * LC * * - - * - - V Skhyly Kohylnyka; Kuchurhan E Krymski Hory DD - - - DD * * - * - - - - * - - - - * - - - - - - * - - - - - V Osovynskyi Step; ТепеОба; Karadah V Khomutovskyi Step; Mykhailivskyi Step V Karadah - * * - E – E Krymski Hory * Chamaecyisus graniicus (Rehmann.) Rothm. Chamaecyisus podolicus (Błocki) Klásková Chamaecyisus wulii (V.Krecz.) Klásková Cochlearia polonica * Frohl. Colchicum fominii Bordz. * Comperia comperiana (Steven) Asch. et Graebn. Crambe aspera M.Bieb. Crambe grandilora DC. * Crambe koktebelica (Junge) N.Busch Crambe mitridais Juz. * * * Crambe pinnaiida W.T.Aiton Crambe steveniana Rupr. Crambe tataria Sebeok Crataegus pojarkovae Kossych Crocus banaicus Gay Cyclamen kuznetzovii Kotov et Czernowa * * * * * 7 RDBU - * BC - Res 6 - - Cephalaria demetrii Bobrov Cephalaria litvinovii Bobrov Cerasus klokovii Sobko A(iv) - IUCN db 2015-4 - * Caragana scythica (Kom.) Pojark. Carex secalina Wahlenb. - Chyvchyny; Marmaroski Hory; Chornohora; Dzhohul V Korsak-Mohyla A(iii) - Taxon A(i) RBEB * IPAs where the taxon is a criterion of selecion A(ii) Res 6 - * RDBU BC LC A(iv) A(ii) IUCN db 2015-4 Campanula serrata (Kit.) Hendrych A(iii) A(i) Taxon IPAs where the taxon is a criterion of selecion V Tepe-Oba; Opuk; Karadah V Osovynskyi Step; Karalarskyi Step; Kazantyp; Ak-Monaiskyi Step; Karadah R Tepe-Oba; Opuk; Karadah V Ak-Monaiskyi Step; Kazantyp; Karalarskyi Step; Tarkhankut; Opuk V Kazantyp; Karadah - - - * - * * - * - - - V - – * - - - - E Dunaiski Plavni * Vu * * - Dianthus pseudoseroinus Błocki Dicranum viride (Sull. et Lesq.) Lindb. Diplotaxis cretacea Kotov - - - - - * * V - - - - Dracocephalum austriacum L. Dracocephalum ruyschiana L. Echium russicum G.F.Gmel. Eleocharis carniolica W.D.J.Koch Eremurus tauricus Steven Erysimum hungaricum * Zapał. Erysimum krynkense Lavrenko Erysimum ucrainicum J.Gay * - * * - * - * - - * - - * - V Dolyna Mertvovodu; Hranitno-Stepove Pobuzhia; Dolyna Inhulu V Levkivski Lisy; Shatski Ozera - Chyvchyny; Marmaroski Hory; Chornohora V Striltsivskyi Step; Kreidiana Flora; Oskilski Skhyly; Marina Hora V Horodnytski Tovtry; Hostra Skelia I Potashnianski Lisy; Kolivska Ulohovyna - – * LC * * - V – Vu - - - E Krymski Hory; Karadah - – * - - - - E – * - - - - V Oskilski Skhyly; Balakyrivka * * * * * 8 Genista tetragona Besser * Gladiolus palustris Gaud. Goniolimon graminifolium (Ait.) Boiss. Goniolimon rubellum (S.G.Gmel.) Klokov * * * - - * DD * * - * Vu DD - * - * - - - - - - - - - - - - - - - * * - * - - - - E Kreidiani Vidslonennia * - - - - E Novobila; Sharivka - - - E R Svydovets; Chornohora * - * * - V Krymski Hory; Karadah * - - - - V Naholnyi Kriazh * - - * - V Sviai Hory - - * - - Irpinskyi Lis, Ternava – Dnister; Pohorylivka; Kadubivska Sinka * * * Gymnospermium odessanum (DC.) Takht. * Gypsophila thyraica Krasnova Hamatocaulis verniculosus (Mit.) Hedenas Hedysarum cretaceum Fisch. Hedysarum ucrainicum Kaschm. Heterophyllium affine (Mitt.) Fleisch. Himantoglossum caprinum (M.Bieb.) C.Koch Hyacinthella pallasiana (Steven) Losinsk. Iris humilis Georgi (Iris pineicola Klokov) Iris hungarica Waldst. & Kit. - * * * * * 9 RDBU * * - * * RBEB Daphne taurica Kotov Delphinium rossicum Litv. Delphinium sergii Wissjul. Dendranthema zawadskii (Herbich) Tzvelev Desmatodon cernuus (Hüb.) B. et S. Dianthus bessarabicus Klokov Dianthus hypanicus * Andrz. Festuca porcii Hack. Fritillaria montana Hoppe Res 6 - BC - IUCN db 2015-4 - * A(iv) En * Ferula orientalis L. A(iii) * V Romosh; Tsetsyno, Krymski Hory; Pidlyska Hora E Vovchanski Skyly; Kolodiazne E Krymski Hory V Dnipro-Oril V Provalskyi Step; Dolyna Mertvovodu R – Taxon A(i) RBEB - IPAs where the taxon is a criterion of selecion A(ii) Res 6 * * RDBU BC * A(iv) IUCN db 2015-4 Daphne sophia Kalen. - A(iii) A(i) Cypripedium calceolus L. A(ii) Taxon IPAs where the taxon is a criterion of selecion - Molochnyi Lyman; Askania-Nova V Chyvchyny; Chornohora E Shebutynskyi Yar; Vasylivskyi i Rozkopynskyi Yary; Kaplivka; Podvirivka E Trosianets E – V Nyzhniodniprovski Pisky; Volyzhyn Lis V Arabatska Strilka; Mytrofanivskyi Pivostriv; Bereh Syvashyka V Hranitno-Stepove Pobuzhia, Mykhailivskyi Step V Verbetska Tovtra; Kadubivska Sinka; Tovtrivska Sinka; Pohorylivka; Probabyn - Marmaroski Hory; Svydovets; Chornohora - - - - E Kedryn DD - - - Cr * * - V Arabatska Strilka; Skhidnyi Churiuk; Mytrofanivskyi Pivostriv E Tepe-Oba - - * - V Chyvchyny; Bushchanske Boloto - - - - V Tiup-Tarkhan i Kalynivskyi Pivostriv * Lindernia procumbens (Krock.) Borb. Liparis loeselii (L.) Rich. * LC * - - * - * * - Mannia triandra (Scop.) Grolle Marsilea quadrifolia L. Medicago kotovii Wissjul. * Medicago saxailis * M.Bieb. Meesia longiseta Hedw. Moehringia hypanica * Grynj et Klokov * - - * - * LC Vu En - * - - Vu * - * * - - * R Ex – - R Dolyna Mertvovodu; Hranitno-Stepove Pobuzhia - - – * * * * * * - 10 - - - V Kreidiana Flora; Riznykivka; Balakyrivka; Skhyly Krasnoi i Kobylky - Dnipro – Oril V Bushchanske Boloto; Bir na Merli - Chornohora; Uholka – Shyrokyi Luh V – - Byriuchyi Ostriv I Krymski Hory RBEB V Krymski Hory * - Neckera pennata Hedw. * - - - V - - - - - - - - * - - - - * - - - - * - * * - * - * - - * - * - - * * - * * - - - - - - E Krymski Hory E Krymski Hory; Tepe-Oba; Karadah E – * - - - E - – * - * * - * - - - V V Krymski Hory; Khomutovskyi Step; Striltsivskyi Step; Vitrohon - – * - - - - E Kolivska Ulohovyna * - - - - V – Nigritella carpaica (Zapał.) Teppner, Klein et Zagulski (Gymnadenia carpaica (Zapał.) Teppner & E.Klein) Onobrychis pallasii (Willd.) M.Bieb. Onobrychis vassilczenkoi Grossh. Onosma graniicola Klokov Onosma polyphylla Ledeb. Ophrys oestrifera M.Bieb. Ophrys taurica (Aggeenko) Nevski Orchis provincialis Balb. Orchis punctulata Steven ex Lindl. Ornithogalum amphibolum Zahar. Orthotrichum scanicum Gronv. Paeonia tenuifolia L. Pallavicinia lyelii (Hook.) Carruth. Pinguicula bicolor Woł. (Pinguicula vulgaris L. ssp. bicolor (Woł.) A. et D.Löve) Pinus cretacea (Kalen.) Kondr. * * * * 11 RDBU - * A(iv) * - A(iii) * * A(i) Vu Narcissus angustifolius Curt. Taxon A(ii) - – RDBU - Lepidium turczaninowii * Lipsky Ligularia sibirica (L.) Cass. (L. bucovinensis Nakai) Limonium tschurjukiense (Klokov) Lavrenko ex Klolkov Linaria cretacea Fisch. ex Spreng. Moehringia lateriflora (L.) Fenzl. * * Res 6 * - BC * - IPAs where the taxon is a criterion of selecion IUCN db 2015-4 * RBEB * Res 6 * BC A(iv) A(ii) A(iii) * IUCN db 2015-4 Jurinea cyanoides (L.) Rchb. Lagoseris purpurea (Willd.) Boiss. (Crepis purpurea (Willd.) M.Bieb.) Larix decidua Mill. subsp. polonica (Racib.) A.E.Murray Lepidium syvaschicum Kleopow A(i) Taxon IPAs where the taxon is a criterion of selecion V Dolyna Nartsysiv; Marmaroski Hory; Svydovets - Svydovets; Chornohora; Uholka – Shyrokyi Luh E Chyvchyny; Dzhohul V Krymski Hory; Mehanom; Tepe-Oba; Karadah V – E Provalskyi Step; HranitnoStepove Pobuzhia V Krymski Hory; Mehanom; Karadah E Krymski Hory; Kazantyp; Mys Marian; Tepe-Oba; Karadah E Krymski Hory * - - * - - Marmaroski Hory; Svydovets * - - - V R – * - - - V - – * LC * * - Pulsailla patens (L.) Mill. (P. laifolia Rupr.) Pyramidula tetragona (Brid.) Brid. Ranunculus lapponicus L. Rheum rhaponicum L. Rhus coriaria L. * Rhododendron luteum Sweet Salvinia natans (L.) All. * - * * - V Sinozhai, Horodnytski Tovtry; Kasova Hora; Horaivka; Pohorylivka I Levkivski Lisy; Sinozhai * - - - V - – * * * Vu - - * * * - - * I * - - Saxifraga hirculus L. Schivereckia podolica (Besser) Andrz. & Besser ex DC. (Draba podolica (Besser) Rupr.) Senecio besserianus Minder. Serratula lycopifolia (Vill.) A.Kern. (Klasea lycopifolia (Vill.) Á.Löve & D.Löve) Serratula tanaitica P.Smirn. * * LC * * * * - * - - – – Krymski Hory; Karadah Olevski Lisy; Yemilchynski Lisy I Dunaiski Plavni; Nyzhnii Dnipro V Bushchanske Boloto I Hostra Skelia; Medobory; Usia – Shutnivtsi; Ternava – Dnister; Marina Hora - - V – * DD * * - - Podvirivka, Vyshnivka * - * * - R – 12 * - * * - RDBU RBEB * Res 6 Silene cretacea Fisch. ex Spreng. BC V Krymski Hory IUCN db 2015-4 - A(iv) - A(iii) RBEB - Taxon A(i) Res 6 Vu IPAs where the taxon is a criterion of selecion A(ii) BC * RDBU IUCN db 2015-4 A(ii) A(iv) Pinus stankewiczii * (Sukacz.) Fomin (P. bruia Ten. var. pityusa (Steven) Silba; P. pityusa Steven var. stankewiczii Sukacz.) Poa graniica BraunBlanq. (Poa deylii Chrtek et V.Jirasek) Pterygoneurum kozlovii Lazar. Pterygoneurum lamellatum (Lindb.) Jur. Pulsatilla grandis Wend. A(iii) A(i) Taxon IPAs where the taxon is a criterion of selecion V Kreidiana Flora; Riznykivka; Skhyly Krasnoi i Kobylky V Hranitno-Stepove Pobuzhia V Krymski Hory Silene hypanica Klokov * - - - - Silene jailensis N.I. Rubtzov Silene sytnikii Krytzka, Novosad et Protopopova * - - - - * - - - - DD * - - LC - - * - - - * * - - – E Zhyzhava; Ternava – Dnister E Krymski Hory * - - - - E – * * - * * - - - * - - - * * * * - V Karadah V Mehanom; Tepe-Oba; Karadah I Kreidiana Flora; Vitrohon V Kreidiana Flora; Marina Hora V – - – - - - - Sisymbrium confertum Steven ex Turcz. Sisymbrium supinum L. Spiraea polonica Błocki Steveniella satyrioides (Steven) Schlechter Sipa anomala P.A.Smirn. Sipa poëica Klokov Stipa syreistschikowii P.A.Smirn. Stipa zalesskii Wilensky Syrenia talievi Klokov Syringa josikaea Jacq. fil. Thesium ebracteatum Hayne Thymus litoralis Klokov et Des.-Shost. * * * * * * * * * * * Tilia dasystyla Steven Tortula handelii Schiffn. Tozzia carpathica Woł. * * DD - * V - Trapa natans L. * LC * - - * 13 V Dolyna Mertvovodu; Hranitno-Stepove Pobuzhia - Krymski Hory V Karalarskyi Step; Arabatska Strilka; Peresyp Aktaskoho Ozera; Opuk E Krymski Hory; Karadah - – - Chyvchyny; Marmaroski Hory; Chornohora I Dunaiski Plavni; Nyzhnii Dnipro BC Res 6 RBEB - Tulipa scythica Klokov et Zoz Typha minima Funk Typha shutleworthii W.D.J.Koch et Sond. Ulota rehmanii Jur. Zostera marina L. * - - - - V Hranitno-Stepove Pobuzhia; Yelanetskyi Step; Mykhailivskyi Step; Dolyna Inhulu; Zelena Balka V Askania-Nova * * - * * - - E Dunaiski Plavni - Chyvchyny * * LC * - E - - – - Molochnyi Lyman; Biriuchyi Ostriv; Arabatska Strilka; Obyichna Kosa RDBU IUCN db 2015-4 - A(iv) - A(ii) - A(iii) * A(i) Tulipa hypanica Klokov et Zoz Taxon IPAs where the taxon is a criterion of selecion Abbreviaions: IUCN db 2015 – version 2015-4 of the IUCN database, BC – Appendix I of the Bern Convenion, Res6 - Resoluion 6 of the Bern Convenion (1998, year of revision 2011), RBEB – Red Data Book of European bryophytes (1995), RDBU – Red Data Book of Ukraine (2009). Note. The scientific names of plants are given mostly according to the checklist of vascular plants of Ukraine (Mosyakin & Fedoronchuk 1999), with necessary taxonomic and nomenclatural adjustments. However, to avoid confusion, we mainly preserved as "main" names of protected species those names which are listed in the official documents mentioned above, even in the cases when new taxonomic and phylogenetic data dictate changes in their nomenclature. For example, some species of Centaurea are currently placed in segregate genera (e.g., Rhaponticoides, Psephellus), some species of Alyssum were recently transferred to Odontarrhena, etc. In all such cases, the names currently accepted by taxonomists are provided after the names used in the IUCN database, Appendix I of the Bern Convention, Resolution 6 of the Steering Committee of the Bern Convention, the Red Data Book of Ukraine, the Red Data Book of European bryophytes, or in other relevant red lists. Since the present book is not a taxonomic treatment, such usage of plant names should not be viewed as endorsement of alternative taxonomic or nomenclatural decisions. Criterion B was applied only for the EUNIS level 2 habitat G1 Broadleaved deciduous woodland. The indicator species checklist of this habitat contains 77 species. All these species have their opimum in this habitat type and constancy <3% in vegetaion data plots of deciduous woods. Most of them are species with small extent of occurence. Analysis of distribuion of indicator species number in deciduous forests of Ukraine shows that the richest 10% of forests are Crimean forests and some forests of the western part of Ukraine with calcareous rocks (Onyshchenko et al. 2008). Six areas have been selected by this criterion: Krymski Hory, Uholka – Shyrokyi Luh, Verkhniobuzki Lisy, Medobory, Karadah, and Mys Marian. Selected areas contain 6% of the habitat G1 in Ukraine. 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 12. 13. 14. 15. 16. 17. 18. 19. 20. 21. 22. 23. 24. 25. 26. 27. 28. 29. 30. 31. 32. 14 Checklist of species for assessment of the botanical richness of habitats type G1: Broadleaved deciduous woodland Taxaceae Taxus baccata L. Ranunculaceae Aconitum besserianum Andrz. ex Trautv. Aconitum degenii Gayer Aconitum gracile (Rchb.) Gayer Aconitum lasiostomum Rchb. Aconitum nemorosum M.Bieb. ex Rchb. Aconitum variegatum L. Aquilegia vulgaris L Cimicifuga europaea Schipcz. (Actaea europaea (Schipcz.) J.Compton) Delphinium pallasii Nevski Helleborus purpurascens Waldst. et Kit. Uricaceae Urica kioviensis Rogov. Caryophyllaceae Cerasium sylvaicum Waldst. et Kit. Brassicaceae Cardamine tenera S.G. Gmel. ex C.A. Mey. Hesperis candida Kit. ex Müggenb., Kanitz et Knapp Hesperis matronalis L. Hesperis steveniana DC. Hesperis sibirica L. Hesperis voronovii N.Busch Primulaceae Cyclamen kuznetzovii Kotov et Czernowa s.str. (Cyclamen coum Mill. s.l.) Lysimachia vericillaris Spreng. Thymeleaceae Daphne sophia Kalen. Daphne taurica Kotov Tiliaceae Tilia dasystyla Stev. Fabaceae Lathyrus laevigatus (Waldst. et Kit.) Fritsch Lathyrus transsilvanicus (Spreng.) Rchb. Lathyrus venetus (Mill.) Wohlf. Rutaceae Dictamnus gymnostylis Stev. Aceraceae Acer stevenii Pojark. Apiaceae Laserpiium laifolium L. Celastraceae Euonymus nanus M.Bieb. Rhamnaceae Rhamnus inctoria Waldst. et Kit. 15 33. 34. 35. 36. 37. 38. 39. 40. 41. 42. 43. 44. 45. 46. 47. 48. 49. 50. 51. 52. 53. 54. 55. 56. 57. 58. 59. 60. 61. 62. 63. 64. 65. 66. 67. 68. Santalaceae Thesium ebracteatum Hayne Oleaceae Syringa josikaea Jacq. il. Rubiaceae Asperula propinqua Pobed. Boraginaceae Solenanthus biebersteinii DC. Solanaceae Scopolia carniolica Jacq. Scrophulariaceae Scrophularia vernalis L. Campanulaceae Adenophora liliifolia (L.) A. DC. Liliaceae Colchicum umbrosum Steven Erythronium dens-canis L. Friillaria ruthenica Wikstr. Nectaroscordum meliophilum (Juz.) Zahar. (Allium siculum Ucria subsp. dioscoridis (Sm.) K.Richt.) Ruscus hypoglossum L. Veratrum nigrum L. Amaryllidaceae Galanthus elwesii Hook. il Leucojum vernum L. Iridaceae Crocus banaicus J. Gay Iris graminea L. Iris hungarica Waldst. et Kit. Iris variegata L. Orchidaceae Anacampis pyramidalis (L.) Rich. Comperia comperiana (Steven) Asch. et Graebn. Corallorhiza triida Châtel. Cypripedium calceolus L. Dactylorhiza romana (Seb. et Mauri) Soó Epipacis atrorubens (Hofm ex Bernh.) Schult. Epipacis microphylla (Ehrh.) Sw. Epipacis purpurata Smith Epipogium aphyllum (F.W.Schmidt) Sw. Himantoglossum caprinum (M.Bieb.) K.Koch Limodorum aborivum (L.) Sw. Ophrys apifera Huds. Ophrys oestrifera M.Bieb. Ophrys taurica (Aggeenko) Nevski Orchis mascula (L.) L. Orchis picta Loisel. Orchis provincialis Balb. 16 69. 70. 71. 72. 73. 74. 75. 76. 77. Orchis punctulata Stev. ex. Lindl. Orchis purpurea Huds. Orchis simia Lam. Steveniella satyrioides (Steven) Schltr. Cyperaceae Carex depauperata Curt. ex With. Carex strigosa Huds. Poaceae Festuca drymeia Mert. et Koch Araceae Arum albispathum Steven ex Ledeb. Arum orientale M.Bieb. Criterion C in our analysis was the presence of habitats from Resluion 4 of the Steering Commitee of the Bern Convenion, 2014 version (table 2). In addiion, one priority habiatat from the Habitats Direcive was used: 4070 Bushes with Pinus mugo and Rhododendron hirsutum (Mugo-Rhododendretum hirsui). The Ukrainian subtype of this habitat (F2.46) is not present in Resoluion 4. For most habitat types we selected maximum ive areas. Main excepions are some habitats correspoding to the priority habitats of the Habiatats Direcive: E1.2 Perennial calcareous grassland and basic steppes (includes 62C0 Ponto-Sarmaic steppes and 6240 Sub-Pannonic steppic grasslands), F3.247 Ponto-Sarmatic deciduous thickets (includes priority habitat type 40C0 Ponto-Sarmatic deciduous thickets), G1.6 Fagus woodland (includes priority habitat type 9150 Medio-European limestone beech forests of the Cephalanthero-Fagion), G1.7 Thermophilous deciduous woodland (includes priority habitat types 91H0 Pannonian woods with Quercus pubescens and 91I0 Euro-Siberian steppic woods with Quercus spp.). The largest number of IPAs are selected for habitat E1.2. Former (and potenial) area of habitat E1.2 in Ukraine is a few tens of imes larger than its current area. At present, the habitat is highly fragmented so ive best sites include only 10% of its area in Ukraine. Besides, ive sites cannot represent the geographical and ecological diversity paterns of steppes. Table 2. Criterion C habitats and corresponding areas. Code A1.11 A1.22 A1.44 A2.2 A2.3 A2.4 A2.5 Name in Resoluion 4 IPAs where the habitat is a criterion of selecion Mussel and/or barnacle – comminiies Mussels and fucoids on moderately – exposed shores Communiies of litoral caves and overhangs Litoral sand and muddy sand Littoral mud Littoral mixed sediments Coastal saltmarshes and saline reedbeds 17 – – – – Molochnyi Lyman; Dzharylhach; Tendrivska Zatoka Code A2.61 A3 A4 A5 B1.1 B1.3 B1.4 (*2130) B1.8 B2.1 B2.3 B3.3 C1.1 C1.222 C1.223 C1.224 C1.225 C1.226 C1.25 C1.32 C1.33 C1.3411 Name in Resoluion 4 IPAs where the habitat is a criterion of selecion Seagrass beds on litoral sediments Infralitoral rock and other hard substrata Circalitoral rock and other hard substrata Sublittoral sediment – Tarkhankut; Mehanom; Tepe-Oba; Opuk – Tendrivska Zatoka; Dzharylhach; Opuk; Mehanom Sand beach dritline Arabatska Strilka; Biriuchyi Ostriv; Obyichna Kosa Shifting coastal dunes Tendrivska Zatoka; Dzharylhach; Arabatska Strilka; Biriuchyi Ostriv Coastal stable dune grassland (grey Tendrivska Zatoka; Dzharylhach; dunes) Arabatska Strilka Moist and wet dune slacks – – Shingle beach driftlines Upper shingle beaches with open – vegetaion Rock clifs, ledges and shores, with Kazantyp; Krymski Hory; angiosperms Mehanom; Tepe-Oba; Opuk Permanent oligotrophic lakes, Shatski Ozera; Bile Ozero; ponds and pools Svydovets; Chornohora Floaing Hydrocharis morsus-ranae – rats Floating Stratiotes aloides rafts Zaplava Prypiai; Zaplava Desny; Zaplavy Dnipra i Sozha Floaing Utricularia australis and Zaplava Desny; Dunaiski Plavni; Utricularia vulgaris colonies Zaplavy Dnipra i Sozha; Nyzhnii Dnipro Floating Salvinia natans mats Dunaiski Plavni; Nyzhnii Dnipro Floating Aldrovanda vesiculosa Zaplava Prypiai; Shatski Ozera; communities Dunaiski Plavni Charophyte submerged carpets in Shatski Ozera mesotrophic waterbodies Free-loaing vegetaion of – eutrophic waterbodies Rooted submerged vegetaion of – eutrophic waterbodies Ranunculus communiies in shallow Zaplava Desny; Dunaiski Plavni; water Nyzhnii Dnipro; Zaplavy Dnipra i Sozha 18 Code C1.3413 C1.44 C1.5 C1.66 C1.67 C2.12 (*7220) C2.18 C2.19 C2.1A C2.1B C2.25 C2.26 C2.27 C2.28 C2.33 C2.34 C3.4 C3.51 C3.55 C3.62 Name in Resoluion 4 Hotonia palustris beds in shallow water Charophyte submerged carpets in dystrophic waterbodies Permanent inland saline and brackish lakes, ponds and pools Temporary inland saline and brackish waters Turlough and lake-botom meadows Hard water springs Acid oligotrophic vegetaion of spring brooks Lime-rich oligotrophic vegetaion of spring brooks Mesotrophic vegetaion of spring brooks Eutrophic vegetaion of spring brooks Acid oligotrophic vegetaion of fastlowing streams Lime-rich oligotrophic vegetaion of fast-lowing streams Mesotrophic vegetaion of fastlowing streams Eutrophic vegetaion of fast-lowing streams Mesotrophic vegetaion of slowlowing rivers Eutrophic vegetaion of slowlowing rivers Species-poor beds of low-growing water-fringing or amphibious vegetaion Euro-Siberian dwarf annual amphibious swards (but excluding C3.5131 Toad-rush swards) Sparsely vegetated river gravel banks Unvegetated river gravel banks 19 IPAs where the habitat is a criterion of selecion – – – – – Krymski Hory; Chyvchyny; Marmaroski Hory; Chornohora – – – – – – – Zaplava Tysy Zaplava Desny; Zaplavy Dnipra i Sozha Nyzhnii Dnipro; Dunaiski Plavni; Zaplava Tysy Zaplava Desny; Zaplavy Dnipra i Sozha; Kanivski Ostrovy; Zaplava Tysy; Ubort – Bolotnytsia Zaplava Desny; Zaplavy Dnipra i Sozha; Kanivski Ostrovy; Zaplava Tysy – – Code Name in Resoluion 4 D2.226 Peri-Danubian black-white-star sedge fens D2.3 Transiion mires and quaking bogs D4.1 D5.2 D6.1 (*1340) E1.11 (*6110) E1.12 E1.13 E1.2 (incl. *6240, *62C0) E1.2 (6210, *Important orchid sites) E1.3 (*6220) IPAs where the habitat is a criterion of selecion Chyvchyny, Chornohora; Svydovets; Marmaroski Hory Perebrody; Somyno; Syra Pohonia; Bile Ozero; Ubort – Bolotnytsia; Cheremske Boloto Rich fens, including eutrophic tall- Pecheniiske Boloto; Zolochivka; herb fens and calcareous lushes Chyvchyny; Bushchanske Boloto; and soaks Kolivska Ulohovyna; Markovychi Beds of large sedges normally Zaplava Desny; Zaplava Prypiai; without free-standing water Zaplavy Dnipra i Sozha; Nyzhnii Dnipro; Dunaiski Plavni Inland saline and brackish marshes Tendrivska zatoka and reedbeds Euro-siberian pioneer rock debris Ternava – Dnister; Zhyzhava; swards Hranitno-Stepove Pobuzhia; Dolyna Inhulu; Dolyna Mertvovodu Euro-Siberian pioneer calcareous – sand swards Coninental dry rocky steppic Kreidiana Flora; Novobila; Oskilski grasslands and dwarf scrub on Skhyly; Vovchanski Skyly chalk outcrops Perennial calcareous grassland and Krymski Hory; Tarkhankut; basic steppes Askania-Nova; Karalarskyi Step; Medvezhanka; Osovynskyi Step; Naholnyi Kriazh; Kalmiuskyi Step; Novobila; Polovetskyi Step; Oskilski Skhyly, Mykhailivskyi Step; Yelanetskyi Step; Davydo-Mykilske; Hranitno-Stepove Pobuzhia; Zelena Balka; Khomutovskyi Step; Dzharylhach; Dolyna Mertvovodu; Dobrianski Hory; Obyichna Kosa; Skhidnyi Churiuk; Striltsivskyi Step; Mehanom; Tepe-Oba; Vitrohon; Provalskyi Step; Ternava – Dnister; Tulyntsi – Makedony; Karadah; Vyshnivka; Kasova Hora; Pohorylivka; Chorna Hora; Yulivski Hory Perennial calcareous grassland and Zholoby; Dubovetski Skhyly basic steppes (Important orchid sites) Mediterranean xeric grassland – 20 Code Name in Resoluion 4 E1.71 (overlaps Nardus stricta swards with *6230) E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland E2.2 E2.3 E3.4 E3.5 E4.11 E4.12 E4.3 (overlaps with *6230) E4.4 E5.4 E5.5 E6.2 F2.22 F2.26 F2.46 (*4070) F3.16 F3.241 (*40A0) IPAs where the habitat is a criterion of selecion Polonyna Borzhava; Chyvchyny Nyzhniodniprovski Pisky; Triokhizbenskyi Step; Kozachelaherska Arena; Dnipro – Oril Low and medium alitude hay Zaplava Desny; Hadiatski Luky; meadows Zaplavy Dnipra i Sozha; Zaplava Siverskoho Dintsia; Stuzhytsia Mountain hay meadows Chyvchyny Moist or wet eutrophic and Zaplava Desny; Zaplavy Dnipra mesotrophic grassland i Sozha; Zaplava Prypiai; Kremenchutski Plavni Moist or wet oligotrophic grassland Zaplava Prypiai; Zaplava Desny; Zaplavy Dnipra i Sozha; Dubrova Boreo-alpine acidocline snow-patch Svydovets; Chornohora; Polonyna grassland and herb habitats Borzhava, Marmaroski Hory Boreo-alpine calcicline snow-patch Svydovets; Chornohora grassland and herb habitats Svydovets; Chornohora; Acid alpine and subalpine grassland Marmaroski Hory; Polonyna Borzhava, Chyvchyny Calcareous alpine and subalpine Chornohora; Svydovets; grassland Chyvchyny; Marmaroski Hory; Moist or wet tall-herb and fern Zaplava Desny; Kanivski Ostrovy; fringes and meadows Zaplavy Dnipra i Sozha; Zaplava Tysy Subalpine moist or wet tall-herb Chornohora; Chyvchyny; and fern stands Svydovets; Marmaroski Hory Continental inland salt steppes Tendrivska Zatoka; Molochnyi Lyman; Dunaiski Plavni; Hrakove; Samarskyi Lis Alpide acidocline Rhododendron Svydovets; Chornohora; heaths Marmaroski Hory; Chyvchyny Bruckenthalia heaths – Carpathian Pinus mugo scrub Chornohora; Chyvchyny; Grofa; Gorgany; Ihrovets - Tavpishyrka Medobory Juniperus communis scrub Central European subcontinental Chorna Hora thickets 21 Code F3.247 (*40C0) F4.2 F5.13 F7 F9.1 Name in Resoluion 4 IPAs where the habitat is a criterion of selecion Krymski Hory; Striltsivskyi Step; Hranitno-Stepove Pobuzhia; Ternava – Dnister; Osovynskyi Ponto-Sarmatic deciduous thickets Step; Kreidiana Flora; Karalarskyi Step; Kamiani Mohyly; Dolyna Mertvovodu; Zhyzhava Dry heaths Polonyna Borzhava; Chyvchyny; Svydovets; Chornohora – Juniper matorral Spiny Mediterranean heaths (phrygana, hedgehog-heaths and related coastal clif vegetaion) Riverine scrub F9.3 Southern riparian galleries and thickets G1.11 (overlaps Riverine Salix woodland with *91E0) Name in Resoluion 4 G1.6 (excluding Fagus woodland (excluding MedioG1.66) European limestone Fagus forests) G1.66 (*9150) Medio-European limestone Fagus forests G1.7 (incl. *91H0, *91I0) Thermophilous deciduous woodland G1.8 Acidophilous Quercus-dominated woodland Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils Ravine and slope woodland Krymski Hory; Tarkhankut; Karadah; Mehanom; Tepe-Oba Zaplava Desny; Zaplavy Dnipra i Sozha; Kanivski Ostrovy; Kremenchutski Plavni Mehanom Zaplava Desny; Zaplavy Dnipra i Sozha; Kremenchutski Plavni; Zaplava Tysy; Kanivski Ostrovy G1.12 (included Boreo-alpine riparian galleries Chyvchyny; Marmaroski Hory; in *91E0) Svydovets; Chornohora G1.21 (included Riverine Fraxinus – Alnus woodland, Zaplava Desny; Zaplavy Dnipra in *91E0) wet at high but not at low water i Sozha; Koncha-Zaspivskyi Lis; Dubrova Zaplava Siverskoho Dintsia; Mixed Quercus – Ulmus – Fraxinus Samarskyi Lis; Zaplava Latorystsi; G1.22 woodland of great rivers Zaplavni Lisy na Borzhavi; Zaplava Desny; Dnipro – Oril G1.3 Mediterranean riparian woodland Zaplava Tysy; Kremenchutski Plavni; Dnipro – Oril; Samarskyi Lis; Kanivski Ostrovy; Zaplava Siverskoho Dintsia G1.4115 Eastern Carpathian Alnus gluinosa – swamp woods G1.414 Steppe swamp Alnus gluinosa Zaplava Siverskoho Dintsia; woods Samarskyi Lis; Zaplavni Lisy na Borzhavi; Sviai Hory; Volyzhyn Lis G1.51 Sphagnum Betula woods Somyno; Morochno-2; Cheremske Boloto 22 Code G1.A1 G1.A4 (incl. *9180) G3.1B G3.1F G3.25 G3.4232 G3.4E G3.5 (incl. *9530) G3.7 G3.9 (incl. *9560) G3.E (*9120) Alpine and Carpathian subalpine Picea forests Enclave Picea abies forests Carpathian Larix and Pinus cembra forests Sarmaic steppe Pinus sylvestris forests Ponto-Caucasian Pinus sylvestris forests Pinus pallasiana and Pinus banaica forests Lowland to montain mediterranean Pinus woodland (excluding Pinus nigra) Coniferous woodland dominated by Cupressaceae or Taxaceae Nemoral bog conifer woodland 23 IPAs where the habitat is a criterion of selecion Krymski Hory; Uholka – Shyrokyi Luh; Skhidne Roztochia; Stuzhytsia; Svydovets Verkhniobuzky Lisy; Tsetsyno; Holohirskyi Lis; Uholka – Shyrokyi Luh Krymski Hory; Savranskyi Lis (91I0); Serbyno (91I0); Yulivski Hory (91H0, 91I0, 91M0); Chorna Hora (91H0, 91M0); Kreidiana Flora (91I0); Potashnianski Lisy (91I0); Dubrova (91I0); Ternava-Dnister (91I0); Levkivski Lisy (91I0); Ardov (91H0) Slovechanskyi Kriazh; Polonskyi Lis; Horodnytskyi Lis; Yemilchynski Lisy Medobory; Chornyi Lis; Homilshanskyi Lis; Brytavskyi Lis; Sviai Hory Medobory; Verkhniobuzki Lisy; Krymski Hory; Marmaroski Hory; Stuzhytsia Chyvchyny; Chornohora; Gorgany; Svydovets; Grofa Cherevaskyi Lis; Rys; Cheremske Boloto; Shatski Ozera Gorgany; Yaiko Perehinske; Kedryn; Ihrovets - Tavpishyrka Sviai Hory; Samarskyi Lis; KonchaZaspivskyi Lis; Bir na Merli Krymski Hory Krymski Hory; Mys Marian Krymski Hory Krymski Hory; Mys Marian; Karahah Syra Pohonia; Ubort – Bolotnytsia; Turova Dacha; Morochno-2; Vtenske Boloto Code H1 Name in Resoluion 4 H2.6 (incl. *8160) Terrestrial underground caves, cave systems, passages and waterbodies Temperate-montane acid siliceous screes Temperate-montane calcareous and ultra-basic screes Acid siliceous screes of warm exposures Calcareous and ultra-basic screes of warm exposures H3.1 Acid siliceous inland clifs H3.2 Basic and ultra-basic inland clifs H3.511 (*8240) X01 X02 X03 X04 (incl. *7110) Limestone pavements Estuaries Saline coastal lagoons Brackish coastal lagoons Raised bog complexes X18 X29 X35 Wooded steppe Salt lake islands Inland Sand Dunes H2.3 H2.4 (incl. *8160) H2.5 IPAs where the habitat is a criterion of selecion – Gorgany; Svydovets; Chornohora; Marmaroski Hory Chyvchyny Арап Р.Я. Методичні аспекти впровадження міжнародної програми "Важливі ботанічні території" в Україні. – К.: Арістей, 2008. – 43 с.] Palmer M., Smart J. Guidelines to the selecion of Important Plant Areas in Europe. Planta Europa, 2001. Red Data Book of European bryophytes, Trondheim, 1995. — 291 pp. Red Data Book of Ukraine. Vegetable kingdom / ed. by Ya.P. Didukh. – Kyiv: Globalconsuling, 2009. – 900 pp. (in Ukr.) [Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с.] – Krymski Hory; Ternava – Dnister; Zhyzhava Hranitno-Stepove Pobuzhia; Dolyna Mertvovodu; Kamiani Mohyly Krymski Hory; Karadah; Ayu-Dah; Tepe-Oba; Ternava – Dnister Krymski Hory; Kazantyp; Chyvchyny – – – Syra Pohonia; Ubort – Bolotnytsia; Morochno-2 – – Kozachelaherska Arena; Triokhizbenskyi Step; Zaplava Prypiai Literature Anderson S. Idenifying Important Plant Areas: a site selecion manual for Europe, and a basis for developing guidelines for other regions of the world. – Plantlife, 2002. – 52 pp. Idenifying and protecing the World's most important plant areas. – Plantlife, 2004. – 7 pp. Kolomiychuk V.P., Onyshchenko V.A., Peregrym M.M. Important plant areas of Azov Region / Ed. T.L. Andrienko. – Kyiv: Alterpress, 2012. – 42 pp. (in Ukr.) [Коломійчук В.П., Онищенко В.А., Перегрим М.М. Важливі ботанічні території Приазов'я / під ред. Т.Л. Андрієнко. – Київ: Альтерпрес, 2012. – 42 с.] Mosyakin S.L., Fedoronchuk M.M. Vascular plants of Ukraine: A nomenclatural checklist. Kiev, 1999. – xxiv + 346 pp. Onyshchenko V.A., Andrienko T.L., Chorney I.I., Kolomiychuk V.P., Didukh Ya.P., Oliiar H.I., Pryadko O.I. Methodical aspects of introducion of internaional program "Important Plant Areas" in Ukraine. – Kyiv: Aristei, 2008 – 43 pp. (in Ukr.) [Онищенко В.А., Андрієнко Т.Л., Чорней І.І., Коломійчук В.П., Дідух Я.П., Оліяр Г.І., Прядко О.І., Вірченко В.М., 24 25 Descripions of IPAs Totally, 173 IPAs were ideniied (maps 1, 2). Their total area is 1 300 774 ha (2.29% of Ukraine with the Territorial sea). The largest areas are “Krymski Hory” (“Crimean Mountains”, 301 150 ha) and “Zaplava Desny” (“Floodplain of the Desna”, 185 741 ha). The smallest area is 4.4 ha. About 55.8% of the total area of IPAs belong to naional and regional (subnaional) protected areas. Overlapping with Emerald Sites is 86.6%. Map 2. Important Plant Areas in Ukraine Aiu-Dah Map 1. Centres of Important Plant Areas in Ukraine 26 V.A. Onyshchenko Ukrainian name: Аю-Даг. Transliteraion/Translaion variants: Ayu-Dag, Ayuv Dağ (Crimean Tatar), Vedmid’-Hora (Ukrainian), Medved’-Gora (Russian). Area: 636.0 ha. Altitude: 0–571 m. Latitude: 44°33’29” N (44.5581°). Longitude: 34°20’09” E (34.3357°). Administrative regions. Autonomous Republic of Crimea: Alushta city (mainly), Yalta city; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 15.3%; B – 1.7%; E – 10.0%; F – 40.0%; G – 25.0%; H – 8.0%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.5%; A2 Littoral sediment – 1.1%; A3 Infralittoral rock and other hard substrata –7.0%; A5 Sublittoral sediment – 6.7%; B2 Coastal shingle – 1.2%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.5%; E1 Dry grasslands – 10.0%; F3 Temperate and mediterranean-montane scrub – 27 15.0%; F5 Maquis, arborescent matorral and thermo-Mediterranean bushes – 25.0%; F6 Garrigue; G1 Broadleaved deciduous woodland – 25.0%; H2 Screes – 1.9%; H3 Inland cliffs, rock pavements and outcrops – 6.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. basic inland clifs; H5.6 Trampled areas. Land use: nature conservaion and research – 100%; tourism/recreaion – major Protected areas: includes Aiu-Dah state landscape reserve (527 ha), overlaps (about 100 ha) with regional hydrological nature monument “Pryberezhnyi Kompleks Bilia Hory Aiudah”. Threats: development (recreaion/tourism) – low, eutrophicaion – low. General description. The IPA is located in the southern part of the Crimea. It includes Mount Ayu-Dah and a 200-m wide strip of the sea. The main rock type is gabbro. A large area is occupied by low (4–5 m) Quercus pubescens and Carpinus orientalis woods with some presence of Fraxinus angusifoliua, Juniperus excelsa, Sorbus domesica. Low shrubby plants of Ruscus ponicus oten form a dense layer. Major species of the herb layer are Poa sterilis and Luzula forsteri. On the top of the mount, main dominant of the tree layer is Quercus petraea. In the herb layer, Poa sterilis and Luzula forsteri are dominants. The Southern slope is covered by low thickets of Juniperus excelsa, Juniperus oxycedrus, Cistus tauricus, Quercus pubescens. Considerable areas are occupied by screes and outcrops. Litoral habitats are represented by shingle beach and rocks. Botanical significance. Main locality of endemic species Brassica taurica (>80% of global populaion). Important area for conservaion of basic outcrops and termophilous deciduous woods. Criterion A(ii) • Brassica taurica (Tzvelev) Tzvelev (Brassica sylvestris Mill. subsp. taurica Tzvelev); A(i); A(ii); abundance: 190 individuals; trend: unknown; species data quality: good; trend data quality: poor. Criterion C • H3.2 Basic and ultra-basic inland cliffs; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 2. Шеляг-Сосонко Ю.Р., Дидух Я.П., Молчанов Е.Ф. Государственный заповедник “Мыс Мартьян”. – Киев: Наук. думка, 1985. – 260 с. Ak-Monaiskyi Step Futher habitat description. A2.1 Litoral coarse sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.3 Mediterranean xeric grassland; F3.2 Submediterranean deciduous thickets and brushes; F5.2 Maquis; F5.3 Pseudomaquis; F6.4 Black Sea garrigues; G1.7 Thermophilous deciduous woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra- 28 V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Ак-Монайський степ. Transliteraion/Translaion variants: Ak-Monaiskii Steppe. Area: 468.0 ha. Altitude: 0–37 m. Latitude: 45°18’53” N (45.3146°). Longitude: 35°36’38” E (35.6104°). Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 16.0%; B – 3.0%; E – 78.0%; H – 3.0%. 29 Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.2%; A2 Littoral sediment – 1.3%; A3 Infralittoral rock and other hard substrata – 2.5%; A5 Sublitoral sediment – 12.0%; B1 Coastal dunes and sandy shores – 0.1%; B2 Coastal shingle – 2.4%; B3 Rock clifs, ledges and shores, including the supralittoral – 0.5%; E1 Dry grasslands – 78.0%; H2 Screes – 0.3%; H3 Inland clifs, rock pavements and outcrops – 1.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Criterion A • Astragalus reduncus Pall.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe grandilora DC.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe mitridais Juz.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Create a state botanical reserve. Arabatska Strilka Futher habitat description. A2.1 Litoral coarse sediment; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.5 Sublitoral macrophyte-dominated sediment; B1.2 Sand beaches above the dritline; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: agriculture (animals) – 30%; tourism/recreaion – minor. Protected areas: overlaps (446 ha) with Emerald Site “Ak-Monaiskyi Steppe”. Threats: –. General description. A part of the southern shore of the Sea of Azov. Major vegetaion type is the steppe dominated by Festuca valesiaca, Koeleria cristata, Sipa brauneri, S. capillata, S. pulcherrima. Other fequent species are Artemisia taurica, Bellevalia sarmatica, Convolvulus cantabrica, Dactylis glomerata, Euphorbia seguierana, Gypsophilla paniculata, Ornithogalum flavescens, Poa bulbosa, Securigera varia, Teucrium chamaedrys, Thalictrum minus, Tragopogon major, Verbascum phlomoides, Xeranthemum annum. By the sea, Crambe pontica, Eringium maritimum, Leymus sabulosus occasionally prevail. There are many calcareous clifs and screes. Botanical significance. Important area for some steppe species, in paricular Astragalus reduncus, Crambe grandilora, Crambe mitridais. V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Арабатська стрілка. Transliteraion/Translaion variants: Arabatska Spit, Arabatska Bar. Area: 12377.0 ha. Altitude: 0–5 m. Latitude: 45°31’26” N (45.5238°). Longitude: 35°11’00” E (35.1831°). Administraive regions. Autonomous Republic of Crimea: Lenine raion. Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 76.5%; B – 2.0%; C – 2.3%; D – 1.0%; E – 17.2%; H – 1.0%. Habitats. Level 2. A2 Littoral sediment – 10.9%; A5 Sublittoral sediment – 65.6%; B1 Coastal dunes and sandy shores – 1.4%; B2 Coastal shingle – 0.6%; C1 Surface standing waters – 2.3%; D6 Inland saline and brackish marshes and reedbeds – 1.0%; E1 Dry grasslands – 13.2%; E6 Salt steppes – 4.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. A2.1 Littoral coarse sediment; A2.2 Littoral sand and muddy sand; A2.3 Littoral mud; A2.4 Littoral mixed sediments; A2.5 Coastal saltmarshes and saline reedbeds; B1.1 Sand beach driftlines; B1.2 Sand beaches above the driftline; B1.3 Shifting coastal dunes; B1.4 Coastal stable dune grassland (grey dunes); B2.1 Shingle beach driftlines; B2.2 Unvegetated mobile shingle beaches above the driftline; C1.5 Permanent inland saline and brackish lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; D6.1 Inland saltmarshes; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E1.2 Perennial calcareous grassland and basic steppes (E1.2G); E6.2 Coninental inland salt steppes; H5.6 Trampled areas. Land use: agriculture (animals) – 20%; forestry – minor; hunting – minor; mowing/hay making – minor; nature conservation and research – major; tourism/recreaion – minor. Protected areas: includes Arabatskyi state landscape reserve (600 ha), included in Ramsar Site “Eastern Syvash”, included in Emeral Site “Eastern Syvash”. Threats: climate change/ sea level rise – medium, development (recreaion/tourism) – low, natural events: erosion – medium. General description. A bar consising of sand and shell with the adjacent waters of the Sea of Azov and Syvash Bay. The sand steppe occupies elevated areas. It is dominated by Agropyron cimmericum, Ephedra distachya, Euphorbia seguierana, Marrubium peregrinum, 30 31 Medicago kotovii, Stipa borysthenica, Sipa capillata, Tortula ruralis. Dominants of halophyic vegetaion are Boloboschoenus mariimus, Elytrigia elongata, Halimione pedunculata, Halimione verrucifera, Halocnemum strobilaceum, Juncus mariimus, Limonium meyeri, Plantago salsa, Puccinellia gigantea, Salicornia perennans, Suaeda prostrata, Tripolium pannonicum, Phragmites australis. On the supralitoral sand and shell, Leymus sabulosus, Crambe mariima, Сakile euxina, Centaurea odessana, Carex colchica, Eryngium maritimum prevail. Large areas of the Syvash are ocuupied by Zostera marina. Botanical significance. Important area for conservaion of sand steppes and brackish aquaic vegetaion. • Goniolimon rubellum (S.G.Gmel.) Klokov; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Lepidium syvaschicum Kleopow; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Thymus litoralis Klokov et Shost.; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Zostera marina L.; A(ii); abundance: abundant; trend: stable; species data quality: good; trend data quality: poor. Criterion C • B1.1 Sand beach driftlines; area: 10 ha; trend: stable; area data quality: medium; trend data quality: medium. • B1.3 Shifting coastal dunes; area: 50 ha; trend: stable; area data quality: medium; trend data quality: medium. • B1.4 Coastal stable dune grassland (grey dunes); area: 90 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Increase area of Arabatskyi state landscape reserve to include all of the IPA. Literature 1. Коломійчук В.П., Абкадирова Е.Ш. Ботанічна і ландшафтна характеристика проектованого ландшафтного заказника “Арабатський степ” // Проблеми фундаментальної і прикладної екології, екол. геології та раціон. природокористування : мат-ли міжнарод. наук.-практ. конфер. – Кривий Ріг: Видавничий Дім, 2009. – С. 290–293. 2. Корженевский В.В., Клюкин А.А. Растительность абразионных и аккумулятивных форм рельефа морских побережий и озер Крыма. – Ялта: ГНБС, 1990. – 108 c. – Деп. в ВИНИТИ 10.07.90, № 3822-В90. 3. Лоскот Н.П. О растительном покрове южной части Арабатской стрелки / Вопросы физиологии, биохимии, цитологии и флоры Украины. – К.: Наукова думка, 1974. – С. 13–16. Ardov Criterion A • Agropyron cimmericum Nevski; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. 32 R.Ya. Kish Ukrainian name: Ардов. Area: 31.0 ha. Altitude: 113–240 m. Latitude: 48°13’59” N (48.2330°). Longitude: 22°39’05” E (22.6514°). Administrative regions. Zakarpatska region: Berehove raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. E – 7.0%; F – 3.4%; G – 88.6%; H – 1.0%. Habitats. Level 2. E1.2 Perennial calcareous grassland and basic steppes – 7.0%; F3 Temperate and mediterranean-montane scrub – 3.4%; G1 Broadleaved deciduous woodland – 88.6%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. F3.1 Temperate thickets and scrub; F3.2 Submediterranean 33 deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Mesoand eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – 90%, nature conservation and research – 81%. Protected areas: includes regional botanical reserve “Ardov” (24.0 ha). Threats: abandonment/reducion of land management – medium. General description. A hill composed of rhyoliic tuf, andesite, basalt, and sedimentary rocks. The main vegetaion type is termophilous oak woods. Dominant of the tree layer is Quercus dalechampii. The shrub layer consists of Cornus mas, Corylus avellana, Euonymus europaeus, Ligustrum vulgare, Pyrus communis, Spiraea media, Swida sanguinea (Cornus sanguinea). In the herb layer, there are Achillea millefolium, Anthericum ramosum, Anthoxanthum odoratum, Brachypodium pinnatum, Campanula patula, Campanula persicifolia, Carex caryophyllea, Carex michelii, Chondrilla juncea, Clinopodium vulgare, Euphorbia cyparissias, Hylotelephium polonicum, Inula ensifolia, Laser trilobum, Melica uniflora, Melittis melissophyllum, Millium efusum, Muscari comosum, Poa nemoralis, Polygonatum odoratum, Potentilla argentea, Potentilla recta, Veronica teucrium, Vincetoxicum hirundinaria, Viscaria viscosa. There are also dry grasslands (with Dianthus carthusianorum, Festuca rupicola, Galathella linosyris, Galium campanulatum, Geranium sanguineum, Melica transsilvanica, Phleum phleoides, Rosa gallica, Seseli annuum, Veronica spicata) and shrubs (Crataegus monogyna s. l., Prunus spinosa, Rosa sp., Spiraea media). Botanical significance. The largest locaion of Habitat Direcive priority habitat 91H0 in Ukraine. Criterion C • G1.7 Thermophilous deciduous woodland (*91H0); area: 24 ha; trend: stable; area data quality: good; trend data quality: medium. 34 Askania-Nova V.A. Onyshchenko Ukrainian name: Асканія-Нова. Area: 11024.0 ha. Altitude: 19–32 m. Latitude: 46°27’47” N (46.4630°). Longitude: 33°57’46” E (33.9628°). Administrative regions. Kherson region: Chaplynka raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.2%; E – 99.8%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.1%; E1 Dry grasslands – 88.0%; E2 Mesic grasslands – 11.0%; E3 Seasonally wet and wet grasslands – 0.8%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes, E2.5 Meadows of the steppe zone, E3.4 Moist or wet eutrophic and mesotrophic grassland. Land use: nature conservation and research – 100%; agriculture (animals) – 20%; tourism/ recreation – minor. Protected areas: included in Askania-Nova biosphere reserve (naional category), AskaniaNova biosphere reserve (UNESCO), and Emerald Site “Askaniia-Nova Biosphere Reserve”. Threats: abandonment / reduction of land management – low, burning of vegetaion – low. General description. One of the largest steppe areas in Ukraine. It represents the southern European steppes on chestnut soils. Main dominants of steppe communities are Stipa ucrainica, Sitpa capillata, Stipa lessingiana, Festuca valesiaca. Species of high constancy: Dianthus andrzejowskianus, Euphorbia seguierana, Falcaria vulgaris, Galium ruthenicum, Goniolimon tataricum, Hylotelephium stepposum, Limonium sareptanum, Phlomoides hybrida (Phlomis hybrida), Phlomis pungens, Potentilla laciniosa, Seseli tortuosum, Verbascum phoeniceum. In depressions, there are mesic grasslands dominated by Poa angustifolia, 35 Alopecurus pratensis, Carex praecox with presence of Achillea micranthoides, Allium regelianum, Euphorbia virgata, Phalacrachena inuloides. In more humid habitats, Elytrigia pseudocaesia and Catex melanostachya dominate. In years with floods they are replaced with Beckmannia eruciformis, Butomus umbellatus, Gratiola officinalis, Lythrum virgatum, Schoenoplectus lacustris. Botanical significance. This area is one of the most important for conservation of steppe vegetation in Europe. Criterion A • Allium regelianum A.Becker ex Iljin; A(ii); abundance: occasional; trend: fluctuating; species data quality: medium; trend data quality: medium. A large part of national population. • Astragalus reduncus Pall.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Centaurea taliewii Kleopow (Rhaponicoides taliewii (Kleopow) M.V.Agab. & Greuter); A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Ferula orientalis L.; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Tulipa scythica Klokov et Zoz; A(iii); abundance: frequent; trend: fluctuating; species data quality: medium; trend data quality: medium. A large part of national population. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 9617 ha; trend: stable; area data quality: good; trend data quality: good. Literature 1. Веденьков Е.П. Флора заповедника “Аскания-Нова” (аннотированный список цветковых растений заповедной степи). – М., 1989. – 52 с. 2. Дрогобыч Н.Е., Шаповал В.В. Распространение редких, исчезающих и эндемичных видов флоры цветковых в заповедной степи “Аскания-Нова”. 2. Эндемичное ядро // Вісті Біосферного заповідника “Асканія-Нова”. – Асканія-Нова, 2004. – Т. 6. – С. 6–13. 3. Ткаченко В.С. Особливості автогенезу асканійського степу // Укр. ботан. журн. – 1990. – 47, № 4. – С. 20–25. 4. Ткаченко В.С., Шаповал В.В. Сукцесії фітосистем ділянки “Північна” новоасканійського заповідного степу у другій половині ХХ і на початку ХХІ ст. // Вісті Біосферного заповідника “Асканія-Нова”. – 2010. – Т. 12. – С. 21–32. 5. Шаповал В.В. БЗ Асканія-Нова імені Ф.Е. Фальц-Фейна // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 13–30. Balakyrivka Ukrainian name: Балакирівка. Area: 266.0 ha. Altitude: 57–140 m. Latitude: 49°20'57" N (49.3490°). Longitude: 38°55'08" E (38.9188°). Administrative regions. Luhansk region: Starobilsk raion. Ownership: state. Biogeographic regions: steppic. V.A. Onyshchenko Habitats. Level 1. E – 78.5%; F – 2.0%; G – 13.9%; H – 5.6%. Habitats. Level 2. E1 Dry grasslands – 78.5%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 13.9%; H2 Screes – 5.6%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial 36 37 calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; forestry – minor; nature conservaion and research – major. Protected areas: includes Balakyrivskyi regional landscape reserve (204 ha), included in Emerald Site "Balakyrivskyi". Threats: agricultural intensification/expansion (arable) – low, extracion (minerals/quarries) – low; forestry (aforestaion) – medium. General description. Slopes of the valleys of the Aidar Rivers with the steppe vegetaion, chalk outcrops, and oak woods. Steppes are dominated by Sipa capillata, Sipa lessingiana, Festuca valesiaca s.l. Dominants of chalk outcrops are Hyssopus cretaceus, Pimpinella titanophila, Thymus cretaceus. Botanical significance. Important area for conservaion of chalk outcrops with endemic species. Criterion A • Erysimum ucrainicum J.Gay.; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. • Linaria cretacea Fisch. ex Spreng.; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. Conservaion proposals. Do not allow aforestaion. Change the status of regional landscape reserve to state botanical reserve. Land use: agriculture (animals) – major; nature conservaion and research – major Protected areas: included in Pryazovskyi naional nature park, overlaps (about 670 ha) with Syvashyk state landscape reserve, included in Emerald Site "Pryazovskyi Naional Nature Park". Bereh Syvashyka V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Берег Сивашика. Transliteraion/Translaion variants: Bereg Sivashika, Coast of Syvashyk. Area: 1646.0 ha. Altitude: 0–8 m. Latitude: 46°22'43" N (46.3786°). Longitude: 35°05'30" E (35.0916°). Administrative regions. Zaporizhia region: Yakymivka raion . Ownership: state (major), private. Biogeographic regions: steppic. Habitats. Level 1. A – 30.7%; C – 23.9%; E – 45.3%; H – 0.1%. Habitats. Level 2. A2 Littoral sediment – 3.9%; A5 Sublittoral sediment – 26.8%; C1 Surface standing waters – 18.0%; C3 Littoral zone of inland surface waterbodies – 5.9%; E1 Dry grasslands – 3.0%; E6 Salt steppes – 42.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.3 Littoral mud; A2.5 Coastal saltmarshes and saline reedbeds; A5.3 Subittoral mud; C3.2 Water-fringing reedbeds and tall helophytes other than canes; E1.2 Perennial calcareous grassland and basic steppes; E6.2 Continental inland salt steppes; H5.6 Trampled areas. 38 Threats: burning of vegetaion – low. General description. Syvashyk is a lagoon of the Sea of Azov. On the litoral of the lagoon and saline lakes, there are salt marshes with Halocnemum strobilaceum, Artemisia santonica, Petrosimonia brachiata, P. oposiifolia, Suaeda salsa, Puccinellia fominii, P. distans. At slightly higher levels, there are salt grasslands dominated by Elytrigia elongata, Limonium meyeri, Juncus gerardii, Apera mariima. On rather steep slopes and on the plateau, there are typical steppes and salt steppes. The typical steppes are dominated by Festuca valesiaca, Koeleria cristata, Sipa capillata, S. ucrainica. Major dominants of the salt steppes are Agropyron pecinatum, Artemisia taurica, Festuca valesiaca s.l., Kochia prostrata. Botanical significance. One of 10 known localiies of Allium regelianum in Ukraine. One of 7 known localiies of Allium pervesitum in Ukraine. 39 Criterion A • Allium pervesitum Klokov; A(i), A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Allium regelianum A.Becker ex Iljin.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Goniolimon rubellum (S.G.Gmel.) Klokov; A(iii); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. Literature 1. Костильов О.В., Устименко П.М., Попович С.Ю. Рослинний покрив заказника "Сивашик" // Укр. ботан. журн. – 1994. – 51, № 5. – С. 115–120. 2. Коломійчук В.П. Ключові ботанічні території Північного Приазов'я // Заповідна справа в Україні. – 2008. – Т. 14, вип. 1. – С. 61–66. 3. Коломійчук В.П., Яровий С.О. Конспект флори судинних рослин Приазовського національного природного парку. – К.: Альтерпрес, 2011. – 296 с. Protected areas: overlaps (8051 ha) with Rivnenskyi nature reserve, overlaps (8051) with Emerald Site "Rivnenskyi Nature Reserve". Bile Ozero V.A. Onyshchenko Ukrainian name: Біле Озеро. Transliteraion/Translaion variants: White Lake Area: 11126 ha. Altitude: 154–165 m. Latitude: 51°30'03" N (51.5008°). Longitude: 25°42'42" E (25.7116°). Administrative regions. Rivne region: Volodymyrets, Zarichne raion; Volynska region: Manevychi raion. Ownership: state, private (minor). Biogeographic regions: continental. Habitats. Level 1. C – 4.2%; D – 38%; E – 0.1%; F – 1.0%; G – 56.7%. Habitats. Level 2. C1 Surface standing waters – 4.2%; D2 – Valley mires, poor fens and transition mires – 25%; D5 Sedge and reedbeds, normally without free-standing water – 13%; E2 Mesic grasslands – 0.1%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 10%; G3 Coniferous woodland – 40.0%; G4 Mixed deciduous and coniferous woodland – 6.7%. Futher habitat description. C1.1 Permanent oligotrophic lakes, ponds and pools; C1.2 Permanent mesotrophic lakes, ponds and pools; D2.3 Transition mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; G1.5 Broadleaved swamp woodland on acid peat; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland, G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland. Land use: forestry – minor, nature conservation and research – 72%; tourism/recreaion – minor. 40 Threats: eutrophicaion – low; water (drainage) – low. General description. Major habitats types are Pinus sylvestris forests and transiion mires. The largest area is occupied by mesic pine forests dominated by Vaccinium myrillus and Pleurozium shreberi. Constant species are Betula pendula, Dicranum polysetum, Melampyrum pratense. On richer soils, diferenial species are Luzula pilosa, Maianthemum bifolium, Quercus robur. Dry pine forests are dominanted by Cladonia gracilis, Cladonia miis, Corynephorus canescens. There also occur swamped Alnus gluinosa woods (oten with dominance of Sphagnum palustre or S. squarrosum), swamped Betula pubescens 41 woods, swamped Pinus sylvestris woods and bogs, wet Alnus gluinosa forests, small areas of Picea abies forests and Carpinus betulus forests. Mires are represented by both mesotrophic and eutrophic ones. The most typical are communiies dominated by Carex lasiocarpa and Carex rostrata with a layer of Sphagnum species (S. cuspidatum, S. fallax, S. lexuosum, S. subsecundum). In the places with a higher water level, Potenilla palustris, Menyanthes trifoliata, Sphagnum teres dominate. Vegetaion of the oligo-mesotrophic karst Lake Bile (453 ha) includes communiies of Chara delicatula, Isoetes lacustris, Myriophyllum spicatum, Nymphaea candida, Phragmites australis, Polygonum amphibium, Potamogeton gramineus, Potamogeton pusillus, Schoenoplectus lacustris (Scirpus lacustris). Botanical significance. Important for conservaion of transiion mires and oligotrophic lakes. Criterion C • C1.1 Permanent oligotrophic lakes, ponds and pools; area: 400 ha; trend: decreasing; area data quality: poor; trend data quality: poor. • D2.3 Transition mires and quaking bogs; area: 1600 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Reduce the intensity of recreaion by Bile Lake. Create state reserves in northeastern and southwestern parts of the IPA that are not yet included in Rivnenskyi nature reserve. Literature 1. Андрієнко Т.Л. ПЗ Рівненський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 313–324. 2. Андрієнко Т.Л., Прядко О.І., Онищенко В.А. Раритетна компонента флори Рівненського природного заповідника // Укр. ботан. журн. – 2006. – 63, № 2. – С. 220– 228. 3. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 215 с. 4. Водно-болотні угіддя України / під ред. Г.Б. Марушевського та І.С. Жарук. – К.: Чорноморська програма Ветландс Інтернешнл, 2006. – 312 с. 5. Орлов О.О., Якушенко Д.М., Борисова О.В. Синтаксономія рослинності озера Біле (Рівненcький природний заповідник) // Збереження та відтворення біорізноманіття природо-заповідних територій: матеріали міжнар. наук.-практ. конф., присвяч. 10-річчю Рівненського природного заповідника (м. Сарни, 11 – 13 черв. 2009 р.) / ред. кол.: М. Д. Будз та ін. – Рівне, 2009. – С. 258–266. 6. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Longitude: 35°14'00" E (35.2335°). Administrative regions. Kharkiv region: Krasnokutsk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1: C – 0.4%, %, D – 0.2%, F – 0.3%, G – 98.1%, H – 1.0%. Habitats. Level 2: C1 Surface standing waters – 0.2%; C3 Littoral zone of inland surface waterbodies – 0.2%; D2 Valley mires, poor fens and transition mires – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.1%; F9 Riverine and fen scrubs – 0.3%; G1 Broadleaved deciduous woodland – 8.1%, G3 Coniferous woodland – 75.0%; G4 Mixed deciduous and coniferous woodland – 15.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion: C1.2 Permanent mesotrophic lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D2.3 Transiion mires and quaking bogs; F9.2 Salix carr and fen scrub; G1.4 Broadleaved swamp woodland not on acid peat; G1.7 Thermophilous deciduous woodland; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.C Mixed Pinus sylvestris – thermophilous Quercus woodland; H5.6 Trampled areas. Bir na Merli O.V. Bezrodnova, N.B. Saidakhmedova Ukrainian name: Бір на Мерлі. Transliteraion/Translaion variants: Pinewoods on the Merla River Area: 2924.0 ha. Altitude: 110–145 m. Latitude: 50°03'44" N (50.0622°). Land use: forestry – minor; nature conservation and research – 100%. Protected areas: included in Slobozhanskyi naional nature park, included in Emerald Site 42 43 "Slobozhanskyi Naional Nature Park". Threats: forestry (intensiied forest management) – low. General description. Terrace of the Merla river with woods and swamps. Pinus sylvestris woods (both natural and plantaions) occupies the largest area. Frequent species are Calamagrosis epigeios, Chamaecyisus ruthenicus, Euonymus verrucosus, Frangula alnus, Genista inctoria, Helichrysum arenarium, Polygonatum odoratum, Sambucus racemosa, Solidago virgaurea, Sorbus aucuparia. In habitats with higher moisture and richness of soil, the fracion of deciduous trees is higher. Typical species are Acer campestre, A. platanoides, A. tataricum, Clinopodium vulgare, Dryopteris carthusiana, Dryopteris ilix-mas, Corylus avellana, Euonymus europaeus, Fragaria vesca, Fraxinus excelsior, Geranium roberianum, Padus avium, Poa nemoralis, Rubus saxailis, Quercus robur, Sambucus nigra, Tilia cordata, Ulmus glabra. In moderately wet Alnus gluinosa woods, frequent species are Aegopodium podagraria, Glechoma hederacea, Galium aparine, Padus avium, Sambucus nigra, Viburnum opulus. The tree layer of swamped woods consists of Alnus gluinosa, Pinus sylvestris, Betula pendula, Betula pubescens, Populus tremula. Dominants of the herb and shrub layers are Carex vesicaria, Filipendula ulmaria, Molinia caerulea, Ribes nigrum, Salix aurita, Salix cinerea, Scirpus sylvaica, Thelypteris palustris, Urica galeopsifolia. In mesotrophic habitats, there occur Carex lasiocarpa, Eriophorum angusifolium, Eriophorum vaginatum, Lycopodium annoinum, Spagnum auriculatum, S. fallax, S. lexuosum, S. girgensohnii, S. palustre, S. subsecundum. Eutrophic and mesotrophic mires without the tree layer occupy smaller areas. Frequent species of sandy glades are Artemisia marschalliana, Psephellus sumensis (Centaurea sumensis), Helichrysum arenarium, Jurinea cyanoides, Koeleria sabuletorum, Oenothera biennis, Rumex acetosella, Thymus pallasianus, Cladonia spp. Botanical significance. One of the largest protected steppe pine woods in Ukraine. Swamps with species that are rare in the forest-steppe zone. There are 6 species from the list of criterion A species: Dracocephalum ruyschiana, Iris humilis, Iris hungarica, Jurinea cyanoides, Liparis loeselii, Pulsailla patens. Criterion A • Liparis loeselii (L.) Rich.; A(ii); rare; trend: decreasing; species data quality: poor; trend data quality: poor. Criterion C • G3.4232 Sarmaic steppe Pinus sylvestris forests; area: 1500 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Безроднова О.В., Саідахмедова Н.Б. Збереження популяції Diphasiastrum complanatum (L.) Holub у НПП "Слобожанський" // Природоохоронні території в минулому, сучасному й майбутньому світі (до 130-річчя створення "Пам’ятки Пеняцької" – першої природоохоронної території у Європі): Матеріали Другої міжнародної наукової конференції (Львів – Броди – Пеняки, 26-27 жовтня 2016 року). – Львів: Ліга-Прес, 2016. – С. 39–42. 2. Саідахмедова Н.Б., Безроднова О.В. Профілі та трансекти // Літопис природи Національного природного парку "Слобожанський" (за 2015 рік). Т. 4. – Краснокутськ, 2016. – С. 13–20 [Рукопис]. 3. Філатова О.В., Саідахмедова Н.Б., Клімов О.В. НПП Слобожанський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 486–495. 44 Bobrovyi Kut V.P. Kolomiychuk Ukrainian name: Бобровий Кут. Area: 30.5 ha. Altitude: 7–23 m. Latitude: 47°05'16" N (47.0877°). Longitude: 32°55'33" E (32.9258°). Administrative regions. Kherson region: Velyka Oleksandrivka raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 91.5%; G – 3.5%; H – 2.0%; J – 3.0%. Habitats. Level 2. E1 Dry grasslands – 91.5%; G1 Broadleaved deciduous woodland – 3.5%; H5 Miscellaneous inland habitats with very sparse or no vegetaion – 2.0%; J3 Acive opencast mineral extracion sites, including quarries – 3.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; G1.C Highly artificial broadleaved deciduous forestry plantations; H5.6 Trampled areas; J3.2 Active opencast mineral extraction sites, including quarries. Land use: agriculture (animals) – major, extracion (minerals) – minor, mowing/hay making – minor. Protected areas: – Threats: agricultural intensiicaion/expansion (grazing) – low, burning of vegetaion – low, 45 extracion (mineral/quarries) – medium. General description. Grassland on the sand terrace of the Inhulets River. Dominant species are Artemisia campestris, Festuca beckeri, Poa bulbosa. Other frequent species are Agropyron lavrenkoanum, Chondrilla juncea, Dianthus platyodon, Echinops ritro, Eragrostis minor, Jurinea sp., Helicrysum arenarium, Koeleria glauca, Plantago scabra, Tortula ruralis, Cladonia sp. Small parts of the area are ariicial wood stands with Robinia pseudoacacia, Ulmus minor, Elaeagnus angusifolia and an illegal sand quarry. Botanical significance. Important area for the narrow endemic species Centaurea paczoskii (one of 2 localiies). Criterion A • Centaurea paczoskii Kotov ex Klokov; A(iii); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Create a state botanical reserve and an Emerald Site. Literature 1.Мойсієнко І.І., Мельник Р.М. Волошка Пачоського Centaurea paczoskii Klokov (C. margaritacea Ten. subsp. paczoskii (Kotov et Klokov) Dostál) / Червона книга України. рослинний світ. / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 306. 2.Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. (Centaurea L.) // Укр. ботан. журн. – 1991. – 48, № 3. – С. 78–80. layer, there prevail Carex brevicollis, Carex pilosa, Corydalis solida, Lamium galeobdolon, sometimes also Convallaria majalis, Hedera helix, Vinca minor. Typical species are Acer campestre, Acer platanoides, Acer tataricum, Aegonychon purpureocaeruleum, Arum besseranum, Cerasus avium, Cornus mas, Euphorbia amygdaloides, Iris graminea, Hedera helix, Melica uniflora, Scutellaria altissima, Stellaria holostea, Swida sanguinea (Cornus sanguinea), Viburnum lantana. Brytavskyi Lis V.A. Onyshchenko Ukrainian name: Бритавський ліс. Transliteraion/Translaion variants: Brytavskyi Forest. Area: 4407 ha. Altitude: 190–281 m. Latitude: 48°10'36" N (48.1767°). Longitude: 29°08'24" E (29.1400°). Administrative regions. Vinnytsia region: Chechelnyk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. G – 99.5%; H – 0.5%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 99.5%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5% . Futher habitat description. G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – major. Protected areas: includes Brytavskyi state botanical reserve (3259 ha), included in Karmeliukove Podillia naional nature park, included in Emerald Site "Karmeliukove Podillia Naional Nature Park". Threats: development (recreaion/tourism) – low. General description. Almost the entire territory is occupied by the broadleaved forest. The tree layer is dominated by Quercus petraea, Quercus robur, Carpinus betulus. In the herb Botanical significance. Well preserved oak-hornbeam forest. Criterion C • G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; area: 4350 ha; trend: stable; area data quality: good; trend data quality: good. Literature 1. Куземко А.А., Яворська О.Г., Ворона Є.І., Чорна Г.А., Федорончук М.М. Ключові території національного рівня на території Вінницької області та їх значення для оптимізації мережі природно-заповідного фонду // Заповідна справа в Україні. – 2010. – т. 16, вип. 1. – С. 88–93. 46 47 Ownership: state, private (minor). Biogeographic regions: coninental. Habitats. Level 1. C – 0.7%; D – 27.7%; E – 19.0%; F – 7.0%; G – 45.6%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C2 Surface running waters – 0.2%; C3 Littoral zone of inland surface waterbodies – 0.4%; D4 Base-rich fens and calcareous spring mires – 15.9%; D5 Sedge and reedbeds, normally without free-standing water – 11.8%; E3 Seasonally wet and wet grasslands – 17.6%; E5 Woodland fringes and clearings and tall forb stands – 1.4%; F9 Riverine and fen scrubs – 7.0%; G1 Broadleaved deciduous woodland – 33.3%; G3 Coniferous woodland – 8.5%; G4 Mixed deciduous and coniferous woodland – 3.8%. Futher habitat descripion. D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; F9.2 Salix carr and fen scrub; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G3.4 Pinus sylvestris woodland south of the taiga; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland. Land use: mowing/hay making – 6%; forestry – minor; nature conservation and research – major. Protected areas: overlaps (about 773 ha) with Dermansko-Ostrozkyi naional nature park, overlaps (265 ha) with Bushchanskyi state botanical reserve; includes Zaplava Zbytynky regional botanical reserve (112.5 ha), includes Boloto Kruhliak regional botanical reserve (32.6 ha), includes Pivdennomosivskyi regional landscape reserve (17.7 ha), overlaps (about 773 ha) with Emerald Site "Dermansko-Ostrozkyi Naional Nature Park". Threats: abandonment/reducion of land management – low. General description. Botom of the Zbytynka river valley with woods and fens. The main vegetaion type is swamp forest dominated mainly by Alnus gluinosa. In the herb layer, there prevail Carex appropinquata, Carex acuiformis, Filipendula vulgaris. Other typical species are Ranunculus repens, Peucedanum palustre, Stachys palustris. Dominants of non-forest mires are Carex rostrata, Carex lasiocarpa, Carex lava, Aulacomium palustre, Drepanocladus aduncus, Hamatocaulis vernicosus, Calliergonella cuspidata. Mires with dominance of Carex lasiocarpa, Sphagnum fallax, S. squarrosum, S. warnstorii occupy a small area. Rich fens are dominated by Schoenus ferrugineus, Carex davalliana, Carex hosiana, Carex lava, Molinia caerulea. On higher ground there is a Pinus sylvestris forest. Botanical significance. Important area for rich fens and Ligularia sibirica, Liparis loeselii, Saxifraga hirculus. Criterion A • Ligularia sibirica (L.) Cass. (L. bucovinensis Nakai); A(ii); rare; trend: unknown; species data quality: medium; trend data quality: poor. • Liparis loeselii (L.) Rich.; A(ii); rare; trend: unknown; species data quality: poor; trend data quality: poor. • Saxifraga hirculus L.; A(ii); rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; area: 140 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Андрієнко Т.Л., Онищенко В.А., Дацюк В.В. НПП Дермансько-Острозький // Фіторізноманіття національних природних парків України / Під заг. ред. Т.Л. Андрієнко та В.А. Онищенка. – Київ: Науковий світ, 2003. – С. 206–214. 2. Головко О.В., Діхтярук В.М., Кальчук Г.В. Аналіз стану популяції Swertia perennis L. (Gentianaceae) на території національного природного парку "ДерманськоОстрозький" // Труды Гос. Никит. ботан. сада. – 2013. – Т. 135. – С. 132–137. 3. Пашкевич Н.А., Блінкова О.І., Козинятко Т.А. Еколого-ценотичні особливості популяції Schoenus ferrugineus L. на території Дермансько-Острозького національного природного парку // Заповідна справа в Україні. – 2013. – 19 (1). – C. 86–88. 48 49 2. Польовий Є.В., Давидов Д.А. Синузія весняних ефемероїдів Бритавського лісу // Наукові записки НаУКМА. – 2016. – Т. 184. – С. 67–71. 3. Яворська О.Г. НПП Кармелюкове Поділля // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 266–272. Bushchanske Boloto O.V. Holovko, V.A.Onyshchenko Ukrainian name: Бущанське болото. Transliteraion/Translaion variants: Bushchanske Fen. Area: 880.0 ha. Altitude: 206–230 m. Latitude: 50°17'55" N (50.2987°). Longitude: 26°12'40" E (26.2057°). Administrative regions. Rivne region: Ostroh raion, Zdolbuniv raion Byriuchyi Ostriv V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Бирючий острів. Transliteraion/Translaion variants: Byryuchiy Island, Biriuchii Ostrov. Area: 13406.1 ha. Altitude: 0–5 m. Latitude: 46°08'59" N (46.1498°). Longitude: 35°08'24" E (35.1400°). Administrative regions. Kherson region: Henichesk raion. Zaporizhia region: Yakymivka raion. Territorial waters of Ukraine. Ownership: state (major), private. Biogeographic regions: steppic. Habitats. Level 1. A– 44.3%; B – 1.2%; C – 4.0%; D – 11.0%; E – 37.0%; G – 1.0%; H – 1.5%. Habitats. Level 2. A2 Littoral sediment – 5.0%; A5 Sublittoral sediment – 39.3%; B1 Coastal dunes and sandy shores – 0.7%; B2 Coastal shingle – 0.5%; C1 Surface standing waters – 3.0%; C3 Littoral zone of inland surface waterbodies – 1.0%; D6 Inland saline and brackish marshes and reedbeds – 11.0%; E1 Dry grasslands – 35.0%; E6 Salt steppes – 2.0%; G1 Broadleaved deciduous woodland – 1.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.5%. Futher habitat description. A2.1 Littoral coarse sediment; A2.2 Littoral sand and muddy sand; A2.4 Littoral mixed sediments; A2.5 Coastal saltmarshes and saline reedbeds; B1.1 Sand beach driftlines; B1.2 Sand beaches above the driftline; B1.3 Shifting coastal dunes; B1.4 Coastal stable dune grassland (grey dunes); B2.1 Shingle beach driftlines; B2.2 Unvegetated mobile shingle beaches above the driftline; C1.5 Permanent inland saline and brackish lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E1.2 Perennial calcareous grassland and basic steppes (E1.2G); E6.2 Coninental inland salt steppes; G1.C Highly ariicial broadleaved deciduous forestry plantations, H5.6 Trampled areas. Land use: agriculture (animals) – major; forestry – minor; hunting – minor; mowing/hay making – 3%; nature conservation and research – major; tourism/recreaion – minor. Protected areas: overlaps (about 10407 ha) with Azovo-Syvaskyi naional nature park, overlaps (about 1220 ha) with Pryazovskyi naional nature park, overlaps (about 10407 ha) with Emeral Site "Azovo-Syvaskyi Naional Nature Park", overlaps (about 1220 ha) with Emeral Site "Pryazovskyi Naional Nature Park". Threats: climate change/ sea level rise – low, development (recreaion/tourism) – low, forestry (aforestaion) – low, natural events: spit erosion – medium. General description. A large spit and adjacent sea. The spit consists of sand and shell. The northwestern side is occupied by Phragmites australis (mainly), Bolboschoenus mariimus, Juncus maritimus. A large area is covered by saline meadows dominated by Puccinellia distans, Puccinellia gigantea, Lepidium laifolium, Elytrigia elongata, Elytrigia pseudocaesia, Tripolium vulgaris, Juncus gerardii. On the elevated areas, there are sand steppes with prevailng Festuca beckeri, Carex colchica, Ephedra distachya, Marrubium peregrinum, Teucrium polium, Stipа borysthenica, Astragalus borysthenicus, Medicago kotovii. Other species of high constancy are Agropyron lavrenkoanum, Agropyron pectinatum, Alyssum hirsutum, Androsace elongata, Сentaurea diffusa, Cynodon dactylon, Secale sylvestre, 50 Silene subconica, Thymus dimorphus, Verbascum pinnatifidum. On the litoral, there dominate Cakile euxina and Salsola ponica. On the beach ridges, dominant species are Leymus sabulosus, Eryngium mariimum, Crambe maritima, Argusia sabirica, Euphorbia seguieriana. In the most saline habitats, there dominate Salicornia perennans (mainly), Suaeda prostrata, Limonium caspium, Halocnemum strobilaceum, Limonium meyeri. The major dominant of the aquaic vegetaion is Zostera marina. It co-dominates with Zostera noltii (Nanozostera nolii), Zannichellia pedunculata, Potamogeton pectinatum (Stuckenia pecinata). Botanical significance. Important area for conservaion of sand steppes, psammophyic species, and brackish aquaic vegetaion. 51 Criterion A • Agropyron cimmericum Nevski; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Agropyron dasyanthum Ledeb.; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Мedicago kotovii Wissjul.; A(i); abundance: occasional; trend: decreasing; species data quality: medium; trend data quality: medium. • Zostera marina L.; A(iv); abundance: abundant; trend: stable; species data quality: good; trend data quality: poor. Criterion C • B1.1 Sand beach driftlines; area: 10 ha; trend: stable; area data quality: medium; trend data quality: medium. • B1.3 Shifting coastal dunes; area: 30 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Reduce the number of ungulates. Literature 1. Dubyna D.V., Neuhauslova Z., Shelyag-Sosonco Ju.R. Coastal vegetation of the "Birjucij Island" Spit in the Azov Sea, Ukraine // Preslia. – Praha, 1994. – Vol. 66. – P. 193–216. 2. Dubyna D.V., Neuhauslova Z., Shelyag-Sosonco Ju.R. Vegetaion of the "Birjucij Island" Spit in the Azov Sea. Sand Steppe Vegetaion // Folia Geobot. Phytotax. – Praha, 1995. – Vol. 30. – P. 1–31. 3. Dubyna D.V., Neuhäuslová Z., Shelyag-Sosonco Ju.R Salt meadows of the Birjuchij Islands Spit in the Azov Sea, Ukraine // Preslia. – Praha, 1996. – Vol. 68. – P. 51–62. 4. Dubyna D.V., Neuhauslova Z., Shelyag-Sosonco Ju.R. Salt meadows (FestucoPuccinellietea) of the "Birjucij Island" Spit in the Azov Sea, Ukraine // Preslia. – Praha, 2000. – Vol. 72. – P. 31–48. 5. Dubyna D.V., Neuhäuslová Z. Salt meadows of the Birjuchij Islands Spit in the Azov Sea. Classes Juncetea maritimi and Bolboschoenetea maritimi // Acta Bot. Croat. – 2000. – Vol. 59, №1. – P. 167–178. 6. Dubyna D.V., Neuhäuslová Z. The vegetation of the Azov-Sivash National Nature Park. Class Thero-Salicornietea (S. Pignatti 1953) R.Tx. in R. Tx. et Oberd. 1958 // Thaiszia. – J. Bot. (Kosice). – 2003. – Vol. 13, №1. – P. 1–30. 7. Коломійчук В.П. Ключові ботанічні території Північного Приазов'я // Заповідна справа в Україні. – 2008. – Т. 14, вип. 1. – С. 61–66. 8. Коломійчук В.П. НПП Приазовський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 5–26. 9. Тищенко О.В. Рослинність приморських кіс північного узбережжя Азовського моря. – Київ: Фітосоціоцентр, 2006. – 156 с. 10. Фіторізноманіття національних природних парків України / Під заг. ред. Т.Л. Андрієнко та В.А. Онищенка. – Київ: Науковий світ, 2003. – 143 с. 52 Cheremske Boloto V.A. Onyshchenko Ukrainian name: Черемське болото. Transliteraion/Translaion variants: Cheremske Mire. Area: 4205 ha. Altitude: 157–160 m. Latitude: 51°31’52” N (51.5310°). Longitude: 25°33’20” E (25.5555°). Administrative regions. Rivne region: Volodymyrets raion; Volynska region: Manevychi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.5%; D – 34%; F – 1%; G – 64.5%. Habitats. Level 2. C1 Surface standing waters – 0.5%; D1 Raised and blanket bogs – 1%; D2 Valley mires, poor fens and transition mires – 32%; D5 Sedge and reedbeds, normally without free-standing water – 1%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 15%; G3 Coniferous woodland – 45.5%; G4 Mixed deciduous and coniferous woodland – 4%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.4 Permanent dystrophic lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D1.1 Raised bogs; D2.3 Transiion mires and quaking bogs; 53 D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; F9.2 Salix carr and fen scrub; G1.4 Broadleaved swamp woodland not on acid peat; G1.5 Broadleaved swamp woodland on acid peat; G1.9 Nonriverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.B Non-riverine Alnus woodland; G3.1 Abies and Picea woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland. Land use: forestry – minor, nature conservation and research – 71%. Protected areas: includes Cheremskyi nature reserve (2975.7 ha), includes Emerald Site “Cheremskyi Nature Reserve” (2975.7 ha). Threats: burning of vegetaion – low, water (drainage) – low. General description. Transiion mire and surrounding forest. The mire is dominated by Carex rostrata, Menyanthes trifoliata, Vaccinium oxycoccos (Oxycoccus palustris), Phragmites australis, Carex appropinquata, Carex lasiocarpa, Sphagnum fallax, oten with the open layer of Betula pubescens. Raised bogs with oppressed Pinus sylvestris occupy about 50 ha. Pinus sylvestris forests occupy the largest area. Typical dominants are Vaccinium myrillus, Pleurozium schreberi, Dicranum polysetum. In drier habitats, there dominate lichens (Cladonia alpestre, C. rangiferina, C. sylvaica, Cetraria islandica). In wet habitats the main dominant of the herb layer is Molinia caerulea. In swamp pine forests, there dominate Eriophorum vaginatum, Ledum palustre, Vaccinium oxycoccos (Oxycoccus palustris), Sphagnum nemoreum, S. fallax, S, centrale. Swampy Alnus gluinosa forests are dominated by Carex riparia, Carex acuiformis, Scirpus sylvaicus, Phragmites australis. In more mesic alder forests, dominant species are Athyrium ilix-femina, Vaccinium myrillus, Deschampsia cespitosa. The IPA includes mesotrophic lakes Redychi (14 ha) and Cheremske (7.7 ha). Botanical significance. One of the largest transiion mires in Ukraine. Criterion C • D2.3 Transition mires and quaking bogs; area: 900 ha; trend: stable; area data quality: medium; trend data quality: poor. • G1.51 Sphagnum Betula woods; area: 500 ha; trend: stable; area data quality: poor; trend data quality: poor. • G3.1F Enclave Picea abies forests; area: 15 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Андриенко Т.Л.,Коніщук В.В. Карта рослинності Черемського природного заповідника // Укр. ботан. журн. – 2003. – 60, № 6. – С. 659–669. 2. Коніщук В.В. Рідкісні види рослин Черемського природного заповідника // Укр. ботан. журн. – 2003. – 60, № 3. – С. 264–272. 3. Коніщук В.В. Хвойні ліси Черемського природного заповідника // Рослинність хвойних лісів України (матеріали робочої наради, Київ, листопад 2003 р). – К.: Фітосоціоцентр, 2003. – С. 111–122. 4. Коніщук В.В. Нові місцезнаходження рідкісних рослин у Черемському природному заповіднику // Заповідна справа в Україні. – Канів, 2004. – Т. 10, Вип. 1–2. – С. 18–23. 5. Коніщук В.В. Раритетна компонента біорізноманіття Черемського природного заповідника // Науковий вісник Волинського державного університету імені Лесі Українки № 11 (Ч. ІІ). – Луцьк: РВВ “Вежа”, 2007 р. – С. 125–132. 6. Коніщук В.В. ПЗ Черемський // Фіторізноманіття заповідників і національних природних парків України. Ч.1. Біосферні заповідники. Природні заповідники / під ред. 54 В.А. Онищенка і Т.Л. Андрієнко. – Київ, 2012. – С. 379–389 7. Коніщук В.В., Коновальчук В.К., Парчук Г.В. Черемське болото – потенційне Рамсарське угіддя: проблеми і перспективи охорони // Вісник національного університету водного господарства та природокористування (збірник наукових праць), Випуск 1 (33). – Рівне, 2006. – С. 28–35. 8. Прядко Е.И. Растительность и стратиграфия болота Черемошского в Западном Полесье / Вопросы физиологии, биохимии, цитологии и флоры Украины. – К.: Наук. думка, 1974. – C. 28–53. 9. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Cherevaskyi Lis V.A. Onyshchenko Ukrainian name: Череваський ліс. Transliteraion/Translaion variants: Cherevaskyi Forest. Area: 466.0 ha. Altitude: 171–188 m. Latitude: 51°17’35” N (51.29305°). Longitude: 25°26’05” E (25.43465°). Administrative regions. Volynska region: Manevychi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 1.0%; G – 98.0%; H – 0.8%; J – 0.2%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 13.0%; G3 Coniferous woodland – 70.0%; G4 Mixed deciduous and coniferous woodland – 15.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.8%; J4 Transport networks and other constructed hard-surfaced areas – 0.2%. Futher habitat descripion. G1.4 Broadleaved swamp woodland not on acid peat; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.1 Abies and Picea woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; H5.6 Trampled areas. Land use: forestry – major. Protected areas: included in Emerald Site “Cherevaskyi Lis”. Threats: forestry (intensiied forest management) – medium. General description. Forest dominated by Pinus sylvestris, Betula pendula, Alnus gluinosa, Picea abies. Botanical significance. The largest locaion of Picea abies forests in the latland part of Ukraine. Criterion C • G3.1F Enclave Picea abies forests; area: 200 ha; trend: decreasing; area data quality: poor; trend data quality: poor. Conservaion proposals. Create a state botanical reserve (or a state forest reserve). 55 scrub – 0.3%; G1 Broadleaved deciduous woodland – 98.1%; H2 Screes – 0.0%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Literature 1. Мельник В.І. Острівні ялинники Українського Полісся. – К.: Наукова думка, 1993. – 104 с. Chorna Hora R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Чорна гора. Transliteraion/Translaion variants: Black Mount, Black Hill. Area: 810 ha. Altitude: 170–565 m. Latitude: 48°09’14” N (48.1538°). Longitude: 23°04’18” E (23.0716°). Administrative regions. Zakarpatska region: Vynohradiv raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. E – 1.1%; F – 0.3%; G – 98.1%; H – 0.5%. Habitats. Level 2. E1 Dry grasslands – 1.1%; F3 Temperate and mediterranean-montane 56 Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes – 0.3%; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.6 Fagus woodland; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.3 Temperate-montane acid siliceous screes; H3.1 Acid siliceous inland clifd; H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – 93%. Protected areas: overlaps (747 ha) with Carpathian biosphere reserve (UNESCO) (includes cluster “Chorna Hora” of the biosphere reserve), overlaps (747 ha) with the Karpatskyi biosphere reserve (naional category), includes state botanical reserve “Chorna Hora” (747 ha, belongs to the biosphere reserve), overlaps (747 ha) with Emerald Site “Carpathian Biosphere Reserve. Threats: abandonment/reducion of land management – low. General description. A hill composed of tuf, andesite, rhyolite, and sedimentary rocks. On the southern slopes, the major vegetaion type is the termophilous oak wood. The tree layer is composed of Quercus petraea, someimes with Quercus dalechampii, Quercus polycarpa, Tilia tomentosa, Fraxinus ornus (single locality in Ukraine). In the shrub layer, there prevail Cornus mas, Crataegus monogyna s. l., Euonymus europaeus, Ligustrum vulgare. Typical species of the herb layer are Aegonychon purpureo-caeruleum, Ajuga genevensis, Anthericum ramosum, Astragalus glycyphyllos, Brachypodium pinnatum, Carex michelii, Clinopodium vulgare, Euphorbia cyparissias, Euphorbia polychroma, Hylotelephium polonicum, Hypericum perforatum, Inula hirta, Lathyrus niger, Melica picta, Melica unilora, 57 Melittis melissophyllum, Poa nemoralis, Polygonatum odoratum, Stellaria holostea, Veronica chamaedrys, Veronica oicinalis, Vincetoxicum hirundinaria. On the nothern slopes there are Fagus sylvaica and mixed Fagus sylvaica – Quercus petraea forests (with Asarum europaeum, Brachypodium sylvaicum, Carex pilosa, Dentaria bulbifera, Galium odoratum, Geranium roberthianum, Lamium galeobdolon, Mercurialis perennis). Grasslands occupy a small area. Dominant species are Festuca pseudodalmaica and Brachypodium pinnatum, there are also Anchusa barellieri, Carduus collinus, Cruciata pedemontana, Ferulago sylvaica, Galium campanulatum, Melica transsilvanica, Phleum phleoides, Potenilla recta, Scabiosa ochroleuca, Sipa transcarpathica, Teucrium chamaedrys, Thymus pannonicus, Tordylium maximum, Trifolium alpestre, Veronica spicata. Botanical significance. The largest locaion of steppe vegetaion and one of the largest locaions of termophilous oak woods in the Transcarpathian part of Ukraine. Criterion C • E1.2 Perennial calcareous grassland and basic steppes (*6240); area: 9 ha; trend: decreasing; area data quality: medium; trend data quality: medium. • F3.241 Central European subcontinental thickets; area: 5 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.7 Thermophilous deciduous woodland (*91H0, 91M0); area: 400 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Do not allow the expansion of shrubs and trees in grasslands. Literature 1. Стойко С.М. Дубові ліси Українських Карпат: екологічні особливості, відтворення, охорона. – Львів, 2009. – 220 с. 2. Фіторізноманіття заповідників і національних природних парків України. Ч.1. Біосферні заповідники. Природні заповідники / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – 406 с. pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Chornohora V.A. Onyshchenko, V.M. Virchenko Ukrainian name: Чорногора. Area: 43124.0 ha. Altitude: 570–2061 m. Latitude: 48°08’03” N (48.1341°). Longitude: 24°32’45” E (24.5458°). Administrative regions. Ivano-Frankivsk region: Verkhovyna raion, Yaremche city; Zakarpatska region: Rakhiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.2%; D – 0.1%; E – 16.0%; F – 6.2%; G – 77.0%; H – 0.5%. Habitats. Level 2. C1 Surface standing waters – 0.0%; C2 Surface running waters – 0.2%; E1 Dry grasslands – 0.1%; E2 Mesic grasslands – 0.1%; E3 Seasonally wet and wet grasslands – 0.1%; E4 Alpine and subalpine grasslands stands – 10.1%; E5 Woodland fringes and clearings and tall forb stands – 5.7%; F2 Arctic, alpine and subalpine scrub – 6.2%; G1 Broadleaved deciduous woodland – 6.5%; G3 Coniferous woodland – 35.3%; G4 Mixed deciduous and coniferous woodland – 35.2%; H2 Screes – 0.0%; H3 Inland cliffs, rock 58 Futher habitat description. C1.1 Permanent oligotrophic lakes, ponds and pools; C1.2 Permanent mesotrophic lakes, ponds and pools; C2.1 Springs, spring brooks and geysers; C2.2 Permanent non-tidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E4.1 Vegetated snow-patch; E4.2 Moss and lichen dominated mountain summits, ridges and exposed slopes; E4.3 Acid alpine and subalpine grassland; E4.4 Calcareous alpine and subalpine grassland; E5.4 Moist or wet tallherb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H2.4 Temperate-montane calcareous and ultra-basic screes; H3.1 Acid silicious inland clifs; 59 H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – minor, forestry – minor, mowing/hay making – minor, nature conservation and research – major, tourism/recreaion – minor. Protected areas: overlaps (about 14537 ha) with Karpatskyi (Carpathian) biosphere reserve (naional category), overlaps (about 14537 ha) with Carpathian biosphere reserve (UNESCO), overlaps (about 14537 ha) with Emerald Site “Carpathian Biosphere Reserve”, overlaps (about 26269 ha) with Karparskyi (Carpathian) naional nature park, overlaps (15402 ha) with World Heritage Site “Primeval Beech Forests of the Carpathians and the Ancient Beech Forests of Germany” (core zone: 2477 ha, bufer zone: 12925 ha), overlaps (about 26269 ha) with Emerald Site “Carpathian Naional Nature Park”. Threats: climate change/sea level rise – low, development (recreaion/tourism) – low. General description. The area includes the highest part of the Ukrainian Carpathians. Major vegetaion type is mixed Picea abies – Fagus sylvaica – Abies alba forests. The herb layer is dominated by Athyrium ilix-femina, Dryopteris dilatata, D. carthusiana, D. ilix-mas, Lamium galeobdolon, Calamagrosis arundinacea, Oxalis acetosella, Rubus hirtus. Other frequent species are Anemone nemorosa, Dentaria glandulosa (Cardamine glandulosa), Geniana asclepiadea, Homogyne alpina, Luzula luzuloides, Luzula sylvaica, Symphytum cordatum, Vaccinium myrillus. Pure Fagus sylvaica forests of similar species composiion occupy a smaller area. Natural pure Picea abies forests predominate at higher alitudes and form the upper limit of the forest vegetaion. Dominants of their herb layer are Calamagrosis arundinacea, Luzula sylvaica, Oxalis acetosella, Vaccinium myrillus. Other frequent species are Athyrium distenifolium, Homogyne alpina, Leucanthemum rotundifolium, Rubus idaeus, Senecio ovatus, Soldanella hungarica, Sorbus aucuparia, Streptopus amplexifolium, Vaccinium viis-idaea. The moss layer is dominated by Dicranum scoparium, Pleurozium schreberi, Polytrichum formosum. In the grasslands of the forest belt, there predominate Agrosis tenuis, Festuca rubra and Nardus stricta. There occur poor and rich fens. In the subalpine belt, the largest area is occupied by Pinus mugo communiies. Besides there are shrubs dominated by Duschekia alnobetula (Alnus alnobetula), Juniperus sibirica. Other important subalpine dominants are Nardus stricta, Deschampsia cespitosa, Vaccinium myrillus, Festuca airoides (F. supina), Calamagrosis villosa. Rhododendron myrifolium heaths are less common. In the wet habitats, there occur communiies of Adenostyles alliariae, Cirsium waldsteinii. There are small areas of bogs, transiion mires, poor and rich fens. On the silicate rocks, there prevail Festuca picta and Poa deylii. Calcareous rocky grasslands dominated by Festuca inarmata (Festuca amethysina s.l.) or Festuca versicolor cover small areas. At the highest alitudes (>1800 m), the typical dominants are Oreojuncus triidus (Juncus triidus), Carex curvula, Carex sempervirens. Botanical significance. The most important area for subalpine habitats and species in Ukraine. Important for oligotrophic aquaic habitats and some species of mosses. Criterion A • Anacamptodon splachnoides (Brid.) Brid.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Botrychium matricariifolium (A. Braun ex Döll) W.D.J.Koch; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Buxbaumia viridis (Moug. ex Lam. et DC.) Brid. ex Moug. et Nestl. (B. indusiata Brid.); A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Campanula abieina Griseb. & Schenk; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. 60 • Campanula serrata (Kit.) Hendrych; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Dicranum viridae (Sull. et Lesq.) Lindb.; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Festuca porcii Hack.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Hamatocaulis vernicosus (Mitt.) Hedenas (Drepanocladus vernicosus (Mitt.) Warnst.); A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Heterophyllium affine (Mitt.) Fleisch; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Mannia triandra (Scop.) Grolle; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Neckera pennata Hedw.; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Tozzia carpathica Woł.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • C1.1 Permanent oligotrophic lakes, ponds and pools; area: 1 ha; trend: stable; area data quality: medium; trend data quality: medium. • C2.12 Hard water springs; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: poor. • D2.226 Peri-Danubian black-white-star sedge fens; area: 5 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.11 Boreo-alpine acidocline snow-patch grassland and herb habitats; area: 10 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.12 Boreo-alpine calcicline snow-patch grassland and herb habitats; area: 1 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.3 Acid alpine and subalpine grassland; area: 4000 ha; trend: stable; area data quality: medium; trend data quality: poor. • E4.4 Calcareous alpine and subalpine grassland; area: 400 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.5 Subalpine moist or wet tall-herb and fern stands; area: 2500 ha; trend: stable; area data quality: medium; trend data quality: poor. • F2.22 Alpide acidocline Rhododendron heaths; area: 30 ha; trend: stable; area data quality: poor; trend data quality: poor. • F2.46 (*4070) Carpathian Pinus mugo scrub; area: 2100 ha; trend: stable; area data quality: good; trend data quality: poor. • F4.2 Dry heaths; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • G1.12 Boreo-alpine riparian galleries; area: 100 ha; trend: stable; area data quality: medium; trend data quality: medium. • G3.1B Alpine and Carpathian subalpine Picea forests; area: 2000 ha; trend: increasing; area data quality: medium; trend data quality: medium. • H2.3 Temperate-montane acid siliceous screes; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Андриенко Т.Л., Каркуциев Г.Н., Прядко Е.И. Гидрофильная растительность 61 верховьев р. Прут // Гидробиол. журн. – 1991. – 27, № 5. – С. 16–22. 2.Біорізноманіття Карпатського біосферного заповідника / Кол. авт., Ред. рада: Я.І. Мовчан, Ф.Д. Гамор та ін. – К.: Інтерекоцентр, 1997. – 711 с. 3.Гамор Ф.Д., Волощук М.І., Антосяк Т.М., Козурак А.В. БЗ Карпатський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 45–72. 4.Карпатський національний природний парк // Киселюк О.І., Приходько М.М., Яворський А.І. та ін. / За ред. М.М.Приходька, О.І. Киселюка, А.І. Яворського. – ІваноФранківськ: Фоліант, 2009. – 672 с. 5.Малиновський К.А. Рослинність високогір’я Українських Карпат. – К.: Наук. думка, 1980. – 280 с. 6.Малиновський К.А., Крічфалушій В.В. Рослинні угруповання високогір’я Українських Карпат. – Ужгород, 2002. – 244 с. 7.Нестерук Ю. Рослинний світ Українських Карпат: Чорногора. Екологічні мандрівки. – Львів: БаК, 2003. – 520 с. 8.Онищенко В.А., Данилик І.І. НПП Карпатський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 273–292. 9.Природа Карпатського національного парку. – К.: Наук. думка, 1993. – 216 с. 10. Флора і рослинність Карпатського заповідника / Стойко С.М., Тасенкевич Л.О., Мілкіна Л.І. та ін. – К.: Наук. думка, 1982. – 220 с. Threats: forestry (intensiied forest management) – low; development (recreaion/tourism) – low. Chornyi Lis V.A. Onyshchenko Ukrainian name: Чорний ліс. Transliteraion/Translaion variants: Black Woods, Black Forest. Area: 6909 ha. Altitude: 168–218 m. Latitude: 48°46’20” N (48.7721°). Longitude: 32°34’21” E (32.5726°). Administrative regions. Kirovohrad region: Znamianka raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.1%; D – 0.1%; E – 0.1%; F – 0.2%; G – 98.3%; H – 1.0%; J – 0.2%. Habitats. Level 2. C1 Surface standing waters – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.1%; E2 Mesic grasslands – 0.1%; G1 Broadleaved deciduous woodland – 98.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%; J4 Transport networks and other constructed hard-surfaced areas – 0.2%. Futher habitat description. G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – major, nature conservation and research – 46%. Protected areas: overlaps with Chornoliskyi state landscape reserve (about 3200 ha), includes Chornoliska state hydrological nature monument (2 ha), included in Emerald Site “Znamianskyi Chornyi Lis”. 62 General description. One of the largest woods in the southern forest-steppe zone of Ukraine. Almost the entire territory is occupied by the dark broadleaved forest. The tree layer is dominated by Quercus robur, Fraxinus excelsior, Carpinus betulus, sometimes by Acer campestre, Acer platanoides, Tilia cordata. Main dominants of the herb layer in summer are Aegopodium podagraria, Stellaria holostea, on slopes oten also Carex pilosa. In spring there prevail Allium ursinum, Anemone ranunculoides, Corydalis cava, Corydalis solida, Ficaria verna. Other typical species are Alliaria petiolata, Asarum europaeum, Corylus avellana, Euonymus europaeus, Euonymus verrucosus, Galium aparine, Gagea lutea, Galium odoratum, Geum urbanum, Polygonatum multiflorum, Pulmonaria obscura, Scilla siberica, Ulmus glabra, Urtica dioica, Viola odorata. An interesting object in this area is a small mire which is one of the southernmost localities of Sphagnum in Ukraine (Chornoliska state hydrological nature monument). Botanical significance. Rather well preserved broadleaved forest, one of the best in Ukraine. Criterion C 63 • G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; area: 5900 ha; trend: stable; area data quality: good; trend data quality: good. Conservaion proposals. Create an Emerald Site. Do not allow clearcuing. Literature 1. Мирза-Сіденко В.М., Андрієнко Т.Л., Онищенко В.А., Прядко О.І. Флора і рослинність проектованого Чорнолісько-Дмитрівського національного природного парку // Укр. ботан. журн. – 2008. – 65, № 3. – С. 352–369. 2. Наумович Г.О., Ходосовцев О.Є. Лишайники Чорного лісу (Знам’янський район, Кіровоградська область) // Чорноморський ботанічний журнал. – 2008. – 4, № 1. – С. 7–13. 3. Онищенко В.А., Андрієнко Т.Л. Майбутній національний парк // Заповідні куточки Кіровоградської землі. – К.: Арктур-A, 1999. – С. 131–134. 4. Онищенко В.А., Сіденко В.М. Класифікація лісової рослинності ур. Чорний ліс (Знам’янський район Кіровоградської області) // Наук. вісник Чернівецького університету. – Вип. 145. – Сер.: Біологія, 2002. – С. 178–194. Chortova Hora Ukrainian name: Чортова гора. Transliteraion/Translaion variants: Devil’s Hill. Area: 12 ha. V.A. Onyshchenko, N.V. Shumska Ownership: state. Biogeographic regions: coninental Habitats. Level 1. E – 100.0%; H – 0.0%. Habitats. Level 2. E1 Dry grasslands – 99.0%; E7 Sparsely wooded grasslands – 1.0%; H3 Inland cliffs, rock pavements and outcrops – 0.0%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; E7.2 Sub-coninental parkland; H3.2 Basic and ultra-basic inland cliffs. Land use: nature conservation and research – major. Protected areas: same as Chortova Hora state botanical nature monument. Threats: abandonment/reducion of land management – low. General description. A hill with grasslands dominated by Brachypodium pinnatum, Elytrigia repens, Festuca valesiaca, with presence of Filipendula vulgaris, Fragaria viridis, Salvia pratensis. Botanical significance. The largest populaion of Carlina cirsioides in Ukraine. Criterion A • Carlina cirsioides Klokov; A(iv); abundance: frequent (5000 individuals); trend: stable; species data quality: good; trend data quality: poor. Literature 1. Куковиця Г.С., Дідух Я.П., Шеляг-Сосонко Ю.Р., Абдулоєва О.С. Синтаксономія лучних степів пам’яток природи республіканського значення гг. Касова та Чортова // Укр. фітоцен. зб. – 1998. – Сер. А, Вип. 2 (11). – Київ: Фітосоціоцентр. – С. 42–62. 2. Шумська Н.В., Дмитраш І.І. Поширення та еколого-ценотичні особливості Carlina cirsioides Klok. і Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł. на Бурштинському Опіллі // Флорологія та фітосозологія. – Т. 2. – Київ: Фітон, 2011. – С. 77–81. Chyvchyny Altitude: 290–350 m. Latitude: 49°24’06” N (49.4017°). Longitude: 24°39’54” E (24.6649°). Administrative regions. Ivano-Frankivsk region: Rohatyn raion. 64 I.I. Chorney, V.A. Onyshchenko Ukrainian name: Чивчини. Area: 23177.0 ha. Altitude: 970–1769 m. Latitude: 47°48’23” N (47.8063°). Longitude: 24°52’41” E (24.8780°). Administrative regions. Chernivtsi region: Putyla raion; Ivano-Frankivsk region: Verkhovyna raion. Ownership: state (major), private. Biogeographic regions: alpine. Habitats. Level 1. C – 0.3%; D – 1.0%; E – 15.4%; F – 2.8%; G – 80.2%; H – 0.3%. Habitats. Level 2. C2 Surface running waters – 0.3%; D4 Base-rich fens and calcareous spring mires – 0.8%; D5 Sedge and reedbeds, normally without free-standing water – 0.2%; E1 Dry grasslands – 4.8%; E2 Mesic grasslands – 1.4%; E4 Alpine and subalpine grasslands stands – 2.0%; E5 Woodland fringes and clearings and tall forb stands – 7.2%; F2 Arctic, alpine and subalpine scrub – 2.8%; G1 Broadleaved deciduous woodland – 1.0%; G3 Coniferous woodland – 76.2%; G4 Mixed deciduous and coniferous woodland – 3.0%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. 65 Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent non-tidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland (E1.71 Nardus stricta swards, E1.72 Agrosis – Festuca grassland); D4.1 Rich fens, including eutrophic tall-herb fens and calcareous lushes and soaks; D5.2 Beds of large sedges normally without free-standing water; E3.4 Moist or wet eutrophic and mesotrophic grassland; E4.1 Vegetated snow-patch; E4.2 Moss and lichen dominated mountain summits, ridges and exposed slopes; E4.3 Acid alpine and subalpine grassland; E4.4 Calcareous alpine and subalpine grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H2.4 Temperate-montane calcareous and ultrabasic screes; H3.1 Acid silicious inland cliffs; H3.2 Basic and ultra-basic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements; H5.6 Trampled areas. Land use: agriculture (animals) – minor, forestry – minor, nature conservation and research – major. Protected areas: includes Verkhovynskyi national nature park (12022.9 ha), overlaps (about 6540 ha) with Cheremoskyi national nature park, includes Chornyi Dil state landscape reserve (263 ha), overlaps (about 6300 ha) with Chyvchyno-Hryniavskyi regional landscape reserve, overlaps (about 5890 ha) with Emerald Site “Cheremoskyi”, overlaps (about 14000 ha) with Emerald Site “Verkhovynskyi”. Threats: abandonment/reducion of land management – low, climate change/sea level rise – low. General description. The major vegetaion type is pure Picea abies forest. On rich soils, there dominate Anemone nemorosa, Dentaria glandulosa (Cardamine glandulosa), Calamagrosis arundinacea, Calamagrosis villosa, Oxalis acetosella. Species of signiicant constancy in spruce forests are Athyrium distenifolium, Athyrium ilix-femina, Dicranum scoparium, Dryopteris dilatata, Dryopteris ilix-mas, Euphorbia carniolica, Gymnocarpium dryopteris, Homogyne alpina, Leucanthemum roundifolium, Lonicera nigra, Phegopteris connecilis, Polytrichum formosum, Senecio ovatus, Solidago virgaurea, Sorbus aucuparia, Stellaria nemorum, Streptopus amplexifolius, Symphytum cordatum, Vaccinium myrillus. In some places over the Picea abies belt, there is Pinus mugo scrub. Mesic grasslands of the forest belt are dominated by Cynosurus cristatus, Festuca rubra, Festuca pratensis, Agrostis capillaris, Anthoxanthum odoratum, Dactylis glomerata. Their typical species are Gymnadenia conopsea, Dactylorhiza majalis, Listera ovata (Neoia ovata), Traunsteinera globosa, Campanula serrata. At higher alitudes, the main dominant of grasslands is Nardus stricta, species of high constancy are Agrostis capillaris, Arnica montana, Avenella flexuosa, Deschampsia cespitosa, Hypochaeris uniflora, Luzula luzuloides, Scorzonera rosea, Sieglingia decumbens, Vaccinium myrtillus, Vaccinium vitis-idaea. A common vegetaion type is subalpine Deschampsia caespitosa grasslands (with Arnica montana, Bistorta officinalis, Calamagrostis arundinacea, Festuca rubra, Geranium alpestre, Hypericum maculatum, Luzula luzuloides, Phleum alpinum, Poa chaixii, Scorzonera rosea, Viola declinata). Smaller areas are dominated by Petasites kablikianus (along streams), Festuca saxailis and Festuca carpaica (on stony calcareous soil). There occur calcareous outcrops with rare species (Aster alpinus, Saxifraga luteoviridis, Saxifraga aizoides, Silenananthe zawadskii, Ptarmica tenuifolia, Festuca saxatilis, Silene dubia, Jovibarba preissiana, Campanula kladniana, Cystopteris alpina), rich fens dominated by Carex paniculata and Carex lava; raised bogs, subalpine small shrubs communiies dominated by Juniperus sibirica, Vaccinium myrtyllus, Vaccinium uliginosum; hard water springs and streams with Doronicum carpaicum; acid springs and streams with Cardamine opizii and Saxifraga stellaris (Micranthes stellaris). Botanical significance. Rich in endemic species part of the Carpathians. Important area for mountain spruce forests and subalpine vegetaion. Criterion A • Botrychium matricariifolium (A. Braun ex Döll) W.D.J.Koch; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Botrychium multifidum (S.G.Gmel.) Rupr.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Campanula abieina Griseb. & Schenk; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Campanula serrata (Kit.) Hendrych; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Dicranum viride (Sull. et Lesq.) Lindb.; A(ii); abundance: occasional; trend: unknown; species data quality: poor; trend data quality: poor. • Festuca porcii Hack.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Ligularia sibirica (L.) Cass. (L. bucovinensis Nakai); A(ii); rare; trend: unknown; species 66 67 data quality: medium; trend data quality: poor. Nigritella carpatica (Zapał.) Teppner, Klein et Zagulski (Gymnadenia carpatica (Zapał.) Teppner et Klein); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Tozzia carpathica Woł.; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Typha schuttleworthii W.D.J.Koch et Sond.; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • C2.12 Hard water springs; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: poor. • D2.226 Peri-Danubian black-white-star sedge fens; area: 15 ha; trend: stable; area data quality: poor; trend data quality: poor. • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous lushes and soaks; area: 150 ha; trend: stable; area data quality: poor; trend data quality: poor. • E1.71 Nardus stricta swards; area: 130 ha; trend: stable; area data quality: poor; trend data quality: poor. • E2.3 Mountain hay meadows; area: 100 ha; trend: stable; area data quality: medium; trend data quality: poor. • E4.3 Acid alpine and subalpine grassland; area: 350 ha; trend: stable; area data quality: medium; trend data quality: poor. • E4.4 Calcareous alpine and subalpine grassland; area: 3 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.5 Subalpine moist or wet tall-herb and fern stands; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: poor. • F2.22 Alpide acidocline Rhododendron heaths; area: 1 ha; trend: stable; area data quality: poor; trend data quality: poor. • F2.46 (*4070) Carpathian Pinus mugo scrub; area: 670 ha; trend: stable; area data quality: good; trend data quality: poor. • F4.2 Dry heaths; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • G1.12 Boreo-alpine riparian galleries; area: 100 ha; trend: stable; area data quality: poor; trend data quality: medium. • G3.1B Alpine and Carpathian subalpine Picea forests; area: 20000 ha; trend: increasing; area data quality: medium; trend data quality: medium. • H2.4 Temperate-montane calcareous and ultra-basic screes; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. • H3.511 Limestone pavements; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1.Pawłowski В., Walas J. Les associations des plantes vesculaires des Monts de Czywczyn // Bull. Int. Acad. pol. B. – 1949. – 1. – P. 1–181. 2.Pawłowski В. Ogόlna charakterystyka geobotaniczna Gόr Czywczyńskich // Rozprawy Wydziału Mat.-Przyrodniczego. – Krakόw, 1948. – P. 1–72. 3.Андрієнко Т.Л., Чорней І.І., Онищенко В.А., Буджак В.В. Флора та рослинність проектованого міждержавного україно-румунського біосферного резервату “Мармароські та Чивчино-Гринявські гори” // Укр. ботан. журн. – 2005. – 62, № 4. – С. 589–596. 4.Величко М.В., Чорней І.І. Ботанічна характеристика урочища Мокринів Камінь у Чивчинських горах (Українські Карпати) // Заповідна справа в Україні. – 2003. – Т. 9, вип. 2. – С. 16–18. 5.Величко М.В., Чорней І.І., Буджак В.В. Інвентаризаційний список судинних рослин Чивчинських гір (Українські Карпати) // Наук. вісник Чернівецького ун-ту: Зб. наук. праць. Вип. 223: Біологія. – Чернівці: Рута, 2004. – С. 152–161. 6.Горбик В.П. Лучна рослинність Чивчинських та Гринявcьких гір // Укр. ботан. журн. – 1968. – 25, № 4. – С. 11–17. 7.Горбик В.П. Лісова та чагарникова рослинність Чивчинcьких та Гринявcьких гір // Укр. ботан. журн. – 1968. – 25, № 6. – С. 87–92. 8.Горбик В.П. Ботанічні об’єкти Чивчинських і Гринявcьких гір, що потребують охорони // Мат-ли 5 з’їзду Укр. ботан. тов. – Ужгород, 1972. – С. 133–134. 9.Горбик В.П., Андрієнко Т.Л. Болота Чивчин // Укр. ботан. журн. – 1969. – 26, № 3. – С. 40–44. 10. Загульський М.М., Чорней І.І. Нове місцезнаходження Nigritella nigra (L.) Rich. (Orchidaceae) в Українських Карпатах // Укр. ботан. журн. – 1993. – 50, № 2. – С. 125–129. 11. Малиновський К.А., Крічфалушій В.В. Рослинні угруповання високогір’я Українських Карпат – Ужгород, 2002. – 244 с. 12. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 13. Чопик B.I. Ботаніко-географічна характеристика Чивчино-Гринявських гір в Українських Карпатах // Укр. ботан. журн. – 1969. – 26, № 6. – С. 26–33. 14. Чорней І.І. До питання про ботанічну цінність Чивчинських гір (Українські Карпати) // Наук. вісн. Чернівецького ун-ту: Зб. наук. праць. – Вип. 298: Біологія. – Чернівці: Рута, 2006. – С. 269–273. 15. Чорней І.І., Буджак В.В. Нове місцезнаходження раритетних видів флори у Чивчинських горах (Українські Карпати) // Укр. ботан. журн. – 2003. – 60, № 1. – С. 53–57. 16. Чорней І.І., Буджак В.В., Андрієнко Т.Л. Болота Буковинських Карпат // Укр. ботан. журн. – 2008. – 65, № 2. – С. 180–188. 17. Чорней I.I., Загульський М.М., Смолінська М.О., Королюк B.I. Стан та перспективи охорони рідкісних видів флори у верхів’ї р. Білий Черемош // Екологічні основи оптимізації режиму охорони і використання природно-заповідного фонду. Тез. доп. наук.-практ. конф. – Рахів, 1993. – С. 70–72. 18. Чорней I.I., Токарюк А.І., Буджак В.В. НПП Верховинський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 74–92. 19. Чорней I.I., Токарюк А.І., Буджак В.В. НПП Черемоський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 530–547. 68 69 • Davydo-Mykilske V.A. Onyshchenko, M.M. Peregrym Ukrainian name: Давидо-Микільське. 70 Area: 1580.0 ha. Altitude: 25–150 m. Latitude: 48°30’49” N (48.5136°). Longitude: 39°51’00” E (39.8499°). Administrative regions. Luhansk region: Sorokyne (Krasnodon) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 70.5%; F – 3.0%; G – 26.0%; H – 0.5%. Habitats. Level 2. E1 Dry grasslands – 70.5%; F3 Temperate and mediterranean-montane scrub – 3.0%; G1 Broadleaved deciduous woodland – 25.9%; G3 Coniferous woodland – 0.1%; H2 Screes – 0.5%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; forestry – minor. Protected areas: included in Emerald Site “Sukhodilskyi Regional Landscape Park”. Threats: agricultural intensification/expansion (arable) – low, agricultural intensiicaion/ expansion (grazing) – low, extracion (minerals/quarries) – low, forestry (aforestaion) – medium. General description. Slope of the valley of the Siverskyi Donets river with the steppe vegetaion, forests, and chalk outcrops. Dominants of steppe vegetaion are 4 species of Sipa (S. pulcherrima, S. lessingiana, S. ucrainica and S. capillata), Festuca valesiaca, Caragana frutex, Amygdalus nana and Bothriochloa ischaemum. Signiicant components of the steppe communiies are Salvia nutans, Phlomis pungens, Marrubium praecox, Psephellus marschallianus (Centaurea marschalliana). Plant communiies on chalk are formed by Onosma tanaiica, Artemisia salsoloides, Linum czernjajevii, Ephedra distachya, Euphorbia cretophila, Astragalus albicaulis, Hedysarum grandilorum. Dominants of natural woods are Quercus robur, Fraxinus excelior, Ulmus suberosa, Euonymus verrucosus, Galium aparine, Geum urbanum, Chelidonium majus. There are also a lot of ephemeroids: Ficaria stepporum, Corydalis solida, C. marschalliana, Anemone ranunculoides, Friillaria ruthenica, Tulipa quercetorum, Scilla siberica, Gagea lutea, Gagea minima. Botanical significance. Important area for conservaion of the steppe vegetaion and chalk outcrops. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1120 ha; trend: stable; area data quality: good; trend data quality: poor. Conservaion proposals. Do not allow aforestaion. Create a state botanical reserve an Emerald Site. Literature: 1. Природно-заповідний фонд Луганської області // О.А. Арапов (заг. ред.), Т.B. Сова, О.А. Cавенко, В.Б. Фєрєнц, Н.У. Кравець, Л.Л. Зятьков, Л.О. Морозова. Довідник. – 3-є вид., доп. і перероб. – Луганськ: “Луганська правда”, 2013. – 224 с. 2. Перегрим М.М., Мойсієнко І.І., Перегрим Ю.С., Мельник В.О. Tulipa gesneriana L. (Liliaceae) в Україні. – К.: Видавничо- поліграфічній центр “Київський університет”, 2009. – 135 с. 71 Administrative regions. Dnipropetrovsk region: Dnipropetrovsk raion, Petrykivka raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 17.0%; D – 1.0%; E – 39.4%; F – 0.2%; G – 40.8%; H – 0.5%; I – 1.1%. Habitats. Level 2. C1 Surface standing waters – 8.0%; C2 Surface running waters – 8.0%; C3 Littoral zone of inland surface waterbodies – 1.0%; D5 Sedge and reedbeds, normally without free-standing water – 1.0%; E1 Dry grasslands – 16.7%; E2 Mesic grasslands – 5.9%; E3 Seasonally wet and wet grasslands – 15.8%; E6 Inland salt steppes – 1.0%; F9 Riverine and fen scrubs – 0.2%; G1 Broadleaved deciduous woodland – 28.9% G3 Coniferous woodland – 11.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%; I1 Arable land and market gardens – 1.1%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; D6.1 Inland saltmarshes; E1.2 Perennial calcareous grassland and basic steppes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E2.5 Meadows of the steppe zone; E3.4 Moist or wet eutrophic and mesotrophic grassland; E6.2 Coninental inland salt steppes; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.5 Broadleaved swamp woodland on acid peat; G3.4 Pinus sylvestris woodland south of the taiga; G3.F Highly artificial coniferous plantations. Land use: nature conservation and research – 100%; agriculture (arable) – 1%; mowing / hay making – minor. Protected areas: same as Dniprovsko-Orilskyi Nature Reserve and Emerald Site “DniprovskoOrilskyi Nature Reserve”. Threats: abandonment / reduction of land management – low, burning of vegetaion – low, water (dredging / canalizaion) – low. General description. This is a part of the loodplain and sand terrace over the loodplain on the let bank of the Dnipro in the steppe zone. The loodplain has its looding regime close to natural. Vegetaion of this area is diverse. Forest vegetaion is represented by loodplain Quercus robur woods (400 ha), Populus alba and Populus nigra woods (400 ha), Salix alba woods (80 ha), swamped Alnus gluinosa woods (1–2 ha), Pinus sylvestris and Pinus nigra subsp. pallasiana plantaions (450 ha). Typical species of Quercus robur woods are Ulmus minor (dominantes in the second sublayer of the tree layer), Acer tataricum, Sambucus nigra, Crataegus curvisepala, Alliaria peiolata, Galium aparine, Chaerophyllum temulum, Convallaria majalis, Geum urbanum, Glechoma hederacea, Stellaria media (Alsine media), Torilis japonica, Urica dioica. Typical species of Populus woods are Amorpha fruicosa (invasive), Frangula alnus, Swida sanguinea (Cornus sanguinea), Rubus caesius, Viburnum opulus. Typical species of Salix alba woods: Populus nigra (frequent co-dominant), Cardamine amara, Carex riparia, Equisetum arvense, Iris pseudacorus, Stachys sylvaica. Typical species of Alnus gluinosa woods are Carex acuiformis, Thelypteris palustris. Shrub vegetaion includes communiies of Salix acuifolia (on sands) and Salix cinerea (in waterlogged parts of loodplain). Dry grasslands (670 ha) include sand steppe and open sand grassland. They are dominated by Festuca beckeri, Sipa borysthenica, Artemisia marschalliana, Euphorbia seguieriana, Gypsophila paniculata. Typical species: Allium savranicum, Chamaecyisus borysthenicus, Helichrysum arenarium, Jasione montana, Minuaria piskunovii, Mollugo cerviana, Polygonum arenarium, Salix acuifolia, Jacobaea borysthenica (Senecio borysthenicus), Seseli tortuosum. Floodplain periodically wet grasslands usually are dominated by Festuca regeliana. Typical species: Agrosis stolonifera, Alopecurus pratensis, Calamagrosis canescens, Carex otrubae, Elytrigia repens, Galium physocarpum, Hieracium umbellatum, Inula britannica, Lathyrus pratensis, Poa pratensis, Poa remota, Thalictrum lavum, Vicia tenuifolia, Vicia terasperma. Mesic grasslands are dominated by Poa angusifolia. Saltmarshes are dominated by Elytrigia elongata, Glaux mariima, Limonium hypanicum, Salicornia perennans, Spergularia media. Eutrophic mires are represented mainly by reedbeds dominated by Phragmites australis, Typha laifolia, Typha angusifolia and eutrophic sedge mires dominated by Carex riparia, Carex acuta. Aquaic vegetaion is very diverse. Main dominants: Lemna minor, Lemna trisulca, Nymphaea alba, Nuphar lutea, Salvinia natans, Straiotes aloides, Spirodela polyrrhiza, Trapa borysthenica (T. natans s. l.), Wolia arrhiza. Smaller areas are covered by Ceratophyllum demersum, Potamogeton crispus, Potamogeton lucens, Potamogeton pecinatus (Stuckenia pecinata), Potamogeton perfoliatus. Botanical significance. This area is one of the most important for conservation of loodplain complexes in Ukraine. 72 73 Dnipro – Oril V.A. Onyshchenko Ukrainian name: Дніпро – Оріль. Area: 3766.2 ha. Altitude: 50–73 m. Latitude: 48°30’30” N (48.5083°). Longitude: 34°47’54” E (34.7983°). Criterion A • Agropyron dasyanthum Ledeb.; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Allium savranicum Besser; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Delphinium rossicum Litv.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Lindernia procumbens (Krock.) Borb.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; area: 500 ha; trend: unknown; area data quality: medium; trend data quality: poor. • G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 400 ha; trend: stable; area data quality: medium; trend data quality: poor. • G1.3 Mediterranean riparian woodland; area: 400 ha; trend: unknown; area data quality: medium; trend data quality: poor. Literature 1. Манюк В.В. Эколого-флористические особенности дубрав ДнепровскоОрельського природного заповедника // Питання степового лісознавства та лісової рекультивації земель. – Д.: ДДУ, 1998. – С. 139–146. 2. Манюк В.В. Нарис рослинності Дніпровсько-Орельського природного заповідника // Заповідна справа в Україні. – Канів, 2000. – Т. 6, вип. 1–2. – С. 7–14. 3. Манюк В.В. Структура, типологія, динаміка і відновлення дібров ДніпровськоОрільського природного заповідника. Дис. … канд. биол. наук: 03.00.16. – Д., 2005. – 373 с. 4. Манюк В.В. ПЗ Дніпровсько-Орільський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 102–114. 5. Придюк М.П. Мікобіота Дніпровсько-Орельського природного заповідника / Автореф. дис... канд. біол. наук: 03.00.21. – К., 1999. – 19 с. Dobrianski Hory V.A. Onyshchenko Ukrainian name: Добрянські гори. Transliteraion/Translaion variants: Dobrianski Hills. Area: 1048.0 ha. Altitude: 100–190 m. Latitude: 48°21’28” N (48.3577°). Longitude: 39°23’01” E (39.3836°). Administrative regions. Luhansk region: Lutuhyne raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.1%; E – 93.3%; F – 2.0%; G – 4.2%; H – 0.3%; J – 0.1%. 74 Habitats. Level 2. C1 Surface standing waters – 0.1%; E1 Dry grasslands – 92.0%; E2 Mesic grasslands – 1.3%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 4.2%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.3%; J4 Transport networks and other constructed hard-surfaced areas – 0.1%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; H5.6 Trampled areas. Land use: agriculture (animals) – major, forestry – minor. Protected areas: includes proposed botanical reserve “Dobrianski Hory” (about 100 ha), overlaps with Emerald Site “Dobrianski Hory” (about 108 ha). Threats: agricultural intensification/expansion (arable) – low, agricultural intensiicaion/ expansion (grazing) – low, extracion (minerals/quarries) – low, forestry (aforestaion) – low. General description. A slope of the Luhanchyk river valley. The major habitat type is the steppe. It is dominated by Festuca valesiaca s.l., Sipa capillata, Sipa dasyphylla, Sipa pennata, Caragana frutex. Forests are dominated by Quercus robur, Fraxinus excelior, Ulmus suberosa, Euonymus verrucosus, Galium aparine, Geum urbanum, Ficaria stepporum, Corydalis solida. Prevailng species of the shrub vegetaion are Cerasus fruicosa, Cerasus stepposa, Rosa sp. There are outcrops of sandstone, slate, and coal. Botanical significance. Important area for conservaion of the steppe vegetaion. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 930 ha; trend: stable; area data quality: good; trend data quality: medium. Conservaion proposals. Create a state botanical reserve including the enire IPA. Literature 1. Перегрим М.М. Флора та рослинність проектованого заповідного урочища “Добрянські гори” (Луганська область) // Теоретичні та прикладні аспекти інтродукції рослин і зеленого будівництва: Матеріали ІІ Міжнародної наукової конференції молодих дослідників. – Київ: Фітосоціоцентр, 2002 – С. 65–66. 75 Dolyna Inhulu V.A. Onyshchenko Ukrainian name: Долина Інгулу. Transliteraion/Translaion variants: Ingul Valley, Ingul River Valley. Area: 1243.0 ha. Altitude: 39–81 m. Latitude: 47°46’24” N (47.7734°). Longitude: 32°22’42” E (32.3782°). Administrative regions. Kirovohrad region: Ustynivka raion; Mykolaiv region: Novyi Buh raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 19.6%; D – 0.2%; E – 74.2%; F – 1.0%; G – 4.0%; H – 1.0% . Habitats. Level 2. C1 Surface standing waters – 19.0%; C2 Surface running waters – 0.5%; C3 Littoral zone of inland surface waterbodies – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.2%; E1 Dry grasslands – 71.0%; E2 Mesic grasslands – 3.0%; E3 Seasonally wet and wet grasslands – 0.2%; F3 Temperate and mediterranean-montane scrub – 1.0%; G1 Broadleaved deciduous woodland – 4.0%; H2 Screes – 0.0; H3 Inland cliffs, rock pavements and outcrops – 0.4%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.6%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.3 Permanent eutrophic lakes, ponds and pools; C2.2 Permanent non-idal, fast, turbulent watercourses; C2.3 Permanent non-idal, smooth-lowing watercourses; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.C Highly ariicial broadleaved deciduous forestry plantaions; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – major; forestry – minor; nature conservaion and research – major; water management – minor. Protected areas: overlaps with Pryinhulskyi regional landscape park (1031 ha) and Emerald Site “Pryinhulskyi Regional Landscape Park “ (1031 ha), overlaps with regional hydrological reserve “Soiivske Vodoskhovyshche” (174 ha); includes state zoological reserve “Polozova Balka” (27 ha), regional botanical reserve “Pelaheivskyi” (123.5 ha). Threats: agricultural intensiicaion/expansion (grazing) – low; forestry (aforestaion) – low. General description. The Inhul valley with steppe vegetaion and silicate outcrops. The steppe vegetaion is dominated by Botriochloa ischaemum, Bromopsis inermis, Caragana frutex, Elytrigia intermedia, Elytrigia repens, Carex praecox, Festuca valesiaca, Galatella villosa, Poa angusifolia, Poa bulbosa (in areas with intensive grazing), Spiraea hypericifolia, Sipa capillata, Sipa lessingiana, Sipa pennata, someimes Sipa dasyphylla, Sipa irsa. The most frequent species are Eryngium campestre, Euphorbia seguierana, Festuca valesiaca, Koeleria cristata, Medicago falcata, Potenilla impolita, Teucrium chamaedrys. Petrophyic steppes difer with presence of Achillea ochroleuca, Ceratodon purpureus, Eremogone biebersteinii, Erophila verna, Minuaria setacea, Potenilla incana, Pulsailla pratensis, Sedum acre, Sedum pallasii, Tortula ruralis, Sipa graniicola, meadow steppes – with Caragana frutex, Filipendula vulgaris, Fragaria viridis, Galium verum, Spiraea hypericifolia, Thalictrum minus, true steppes - with Herniaria besseri, Marrubium praecox, Phlomis 76 pungens, Sipa lessingiana, Teucrium polium. Diferenial species of overgrazed steppes are Anthemis ruthenica, Chenopodium album, Grindelia squarrosa (invasive), Poa bulbosa, Salvia aethiopis, Sisymbrium alissimum. In mesic grasslands, there prevail Calamagrosis epigeios, Elytrigia repens, Poa angusifolia, Poa pratensis. The shrub vegetaion is represented mainly by communiies of Acer tataricum and Prunus spinosa s.l. Botanical significance. Important for conservaion of steppe vegetaion, silicious outcrops, endemic petrophyic species. 77 Criterion A • Dianthus hypanicus Andrz.; A(i), A(ii), A(iii), abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Tulipa hypanica Klokov et Zoz; A(iii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.11 Euro-siberian pioneer rock debris swards; area: 2 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 900 ha; trend: stable; area data quality: medium; trend data quality: medium. • F3.247 Ponto-Sarmatic deciduous thickets; area: 3 ha; trend: stable; area data quality: medium; trend data quality: medium. • H3.1 Acid siliceous inland cliffs; area: 4 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Винокуров Д.С. Синтаксономія ксеротермної рослинності р. Інгул (клас FestucoBroetea). Частина І. Петрофітно-степова рослинність. до флори Правобережного степу України // Укр. бот. журн. – 2014. – 71, № 2. – С. 148–160. 2. Винокуров Д.С. Синтаксономія ксеротермної рослинності долини р. Інгул (клас Festuco-Brometea). Частина 2. Лучно-степова, чагарниково-степова, справжньостепова рослинність // Укр. бот. журн. – 2014. – 71, № 5. – С. 538–549. 3. Винокуров Д. Созофіти долини р. Інгул і завдання їх охорони // Вісник Львівського університету. Сер. Біологічна. – 2014. – 65. – С. 135–150. 4. Винокуров Д.С. Синтаксономія вищої водної рослинності долини р. Інгул // Чорноморський бот. журн. – 2011. – 7, № 1. – С. 26–40. 5. Винокуров Д.С. Ключові території Інгульського регіонального екокоридору: характеристика, зв'язки, оптимізація // Чорноморський бот. журн. – 2011. – 7, № 4. – С. 329–346. 6. Екомережа степової зони України: принципи створення, структура, елементи / під ред. Д.В. Дубини і Я.І. Мовчана. – К., 2013. – 409 с. without free-standing water – 0.6%; E1 Dry grasslands – 61.2%; E2 Mesic grasslands – 0.3%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 30.6%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 2.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2% . Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.3 Permanent eutrophic lakes, ponds and pools; C2.2 Permanent non-idal, fast, turbulent watercourses; C2.3 Permanent non-idal, smooth-lowing watercourses; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.C Highly ariicial broadleaved deciduous forestry plantaions; H3.1 Acid silicious inland clifs. Land use: agriculture (animals) – major; forestry – 20%; nature conservaion and research Dolyna Mertvovodu V.A. Onyshchenko Ukrainian name: Долина Мертвоводу. Transliteraion/Translaion variants: Mertvovod Valley, Mertvovod River Valley. Area: 1571.0 ha. Altitude: 23–100 m. Latitude: 47°42’47” N (47.7130°). Longitude: 31°27’21” E (31.4557°). Administrative regions. Mykolaiv region: Arbuzynka raion, Bratske raion, Voznesensk raion. Ownership: state, unknown. Biogeographic regions: steppic. Habitats. Level 1. C – 2.1%; D – 0.6%; E – 61.5%; F – 2.0%; G – 30.6%; H – 3.2% , J – 0.0%. Habitats. Level 2. C1 Surface standing waters – 0.9%; C2 Surface running waters – 0.4%; C3 Littoral zone of inland surface waterbodies – 0.8%; D5 Sedge and reedbeds, normally 78 – 100%. Protected areas: included in Buzkyi Hard Naional Nature Park and Emerald Site “Bugzkyi Gard Naional Nature Park”. Threats: development (recreaion/tourism) – low; forestry (aforestaion) – medium; habitat fragmentaion/isolaion – low. General description. The Mertvovod valley with high (10–60 m) steep slopes and ganite clifs. Large areas are covered by the steppe vegetaion, natural Quercus robur termophilous woods, ariicial Quercus robur, Robinia pseudoacacia woods, steppic and loodplain scrub. Natural deciduous termophilous woods. Dominants: Quercus robur (major), Acer campestre, Fraxinus excelsior, Tilia cordata, Ulmus minor; Acer tataricum, Coinus coggygria, Crataegus 79 fallacina, Euonymus europaeus, Eunymus verrucosus, Swida sanguinea (Cornus sanguinea). Typical species: Malus sylvestris, Pyrus communis; Chelidonium major, Galium aparine, Geum urbanum, Urica dioica. Shrubs. Dominant: Crataegus praearmata, Spiraea crenata, Prunus stepposa. Dry grasslands (steppes). Dominants: Sipa capillata, Sipa lessingiana, Festuca valesiaca, Botriochloa ischaemum Silicious outcrops and screes. Typical species: Achillea ochroleuca, Alyssum murale, Aurinia saxailis, Rumex fascilobus, Sedum acre, Sedum borissovae, Sempervivum ruthenicum, Thymus dimorphus. Botanical significance. Important for conservaion of silicious outcrops with endemic species (Dianthus hypanicus Andrz., Moehringia hypanica Grynj et Klokov, Sedum borissovae Balk., Silene sytnikii Krytzka, Novosad et Protopopova, Tulipa hypanica Klokov et Zoz), termophilous oak woods and steppic scrub. Criterion A • Delphinium sergii Wissjul.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Dianthus hypanicus Andrz.; A(i), A(ii), A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Moehringia hypanica Grynj et Klokov; A(i); abundance: rare (one locality); trend: decreasing; species data quality: good; trend data quality: medium. • Silene sytnikii Krytzka, Novosad et Protopopova; A(iii); abundance: occasional; trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.11 Euro-siberian pioneer rock debris swards; area: 1 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 970 ha; trend: stable; area data quality: medium; trend data quality: medium. • F3.247 Ponto-Sarmatic deciduous thickets; area: 15 ha; trend: stable; area data quality: poor; trend data quality: poor. • H3.1 Acid siliceous inland cliffs; area: 45 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Гревцова Г.Т. Кизильники гранітно-степового Побужжя // Збірник наукових праць Полтавського пед. ун-ту. – 2003. – Вип.4 (31). – С. 54–61. 2. Драбинюк Г.В. НПП Бузький Гард // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 49–60. 3. Новосад В.В., Крицкая Л.И., Протопопова В.В. Новий для науки ендемічний вид Гранітно-степового Побужжя смілка Ситника (Silene sytnikii Krytzka, Novosad et Protopopova), його таксономічні, еколого-ценотичні, хорологічні, генезисні та созологічні особливості // Укр. бот. журн. – 1996. – 53, № 5. – С. 578–585. 4. Партика Л.Я., Вірченко В.М., Нипорко С.О. До бріофлори регіонального ландшафтного парку “Гранітно-степове Побужжя” // Чорномор. ботан. журн. – 2006. – 2, № 1. – С. 116–122. 5. Соломаха В.А., Драбинюк Г.В., Вініченко Т.С., Мойсієнко І.І., Деркач О.М. Адаптивні особливості південнобузьких ендемів Dianthus hypanicus Andrz. та Moehringia hypanica Grynj et Klok. // Укр. фітоцен. зб. – Сер. С. – 2006. – Вип. 24. – С. 70–86. 6. Соломаха В.А., Соломаха Т.Д., Драбинюк Г.В., Мойсієнко І.І. Знахідка Asplenium V.A. Onyshchenko Ukrainian name: Долина Нарцисів. Transliteraion/Translaion variants: Narcissus Valley. Area: 257.6 ha. Altitude: 169–180 m. Latitude: 48°10’57” N (48.1823°). Longitude: 23°21’28” E (23.3575°). Administrative regions. Zakarpatska region: Khust raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. C – 0.4%; D – 12.0%; E – 79.3%; F – 6.0%; G – 2.0%; J – 0.3%. Habitats. Level 2. C2 Surface running waters – 0.4%; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D2 Valley mires, poor fens and transition mires – 9.0%; D5 Sedge and reedbeds, normally without free-standing water – 3.0%; E1 Dry grasslands – 4.0%; E2 Mesic grasslands – 27.0%; E3 Seasonally wet and wet grasslands – 48.0%; E5 Woodland fringes and clearings and tall forb stands – 0.3%; F3 Temperate and mediterranean-montane scrub – 0.2%; F9 Riverine and fen scrubs – 5.8%; G1 Broadleaved deciduous woodland – 2.0%; J4 Transport networks and other constructed hard-surfaced areas – 0.3%. Futher habitat description. C2.3 Permanent non-tidal, smooth-flowing watercourses; D5.1 Reedbeds normally without free-standing water; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E3.5 Moist or wet oligotrophic grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; F3.1 Temperate thickets and scrub; F9.1 Riverine scrub; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; J4.2 Road networks. Land use: mowing/hay making – major, nature conservation and research – major, tourism/ recreaion – minor. Protected areas: included in Karpatskyi (Carpathian) biosphere reserve (naional category), included in Carpathian biosphere reserve (UNESCO), included in Emerald Site “Carpathian Biosphere Reserve “. Threats: –. General description. Floodplain of the river Khustets. The main vegetaion type is 80 81 x alternifolium Wulfen у степовій зоні України // Укр. бот. журн. – 2006. – 63, № 9. – C. 515–517. 7. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 8. Щербакова О.Ф., Новосад В.В., Крицька Л.І. Раритетний флорофонд КодимоЄланецького Побужжя (ЧКУ, 2009): популяційні та флоросозологічні аспекти. Рослинний світ у Червоній книзі України: впровадження Глобальної стратегії збереження рослин. Мат-ли міжнар. конф. (11–15 жовтня 2010 р., м.Київ). – Київ: Альтерпрес, 2010. – С. 210–214. Dolyna Nartsysiv meadows dominated by Molinia caerulea, Deschampsia cespitosa, Narcissus angusifolius, Anthoxanthum odotatum, Festuca ovina, Festuca rubra, Agrostis capillaris, with presence of Betonica officinalis, Centaurea jacea, Filipendula vulgaris, Poa pratensis, Potentilla erecta, Ranunculus acris, Ranunculus repens, Sanguisorba officinalis, Leucanthemum vulgare. Besides there are communniies of Phragmites australis, Iris pseudacorus, Juncus efusus. Along watercourses, there prevail Salix alba, Salix capraea, Salix cinerea, Salix viminalis. Botanical significance. The area includes the largest populaion of Narcissus angusifolius in Ukraine. Narcissus angusifolius dominates in the area of 30 ha. Criterion A Мовчан, Ф.Д. Гамор та ін. – К.: Інтерекоцентр, 1997. – 711 с. 2.Стойко С.М., Тасєнкевич Л.О., Мілкіна Л.І. та ін. Флора і рослинність Карпатського заповідника. – Київ : Наукова думка, 1982 . – 219 с. 3.Устименко П.М., Дубина Д.В., Гамор Ф.Д. Рослинність заповідного масиву “Долина Нарцисів”: сучасний стан та динамічні тенденції // Укр. бот. журн. – 2007. – 64, № 2. – C. 195–205. Dubovetski Skhyly Ukrainian name: Дубовецькі схили. Transliteraion/Translaion variants: Dubovetski Slopes. Area: 4.4 ha. Alitude: 265–315 m. Laitude: 49°05’07” N (49.0854°). Longitude: 24°48’37” E (24.8103°). Subnaional regions. Ivano-Frankivsk region: Halych raion. Ownership: state. • Narcissus angustifolius Curtis; A(ii); abundance: abundant; trend: stable; species data quality: good; trend data quality: medium. Literature 1.Біорізноманіття Карпатського біосферного заповідника / Кол. авт., Ред. рада: Я.І. 82 I.M. Danylyk Biogeographic regions: coninental. Habitats. Level 1. E – 86.0%; F – 10.0%; G – 4.0%. Habitats. Level 2. E1 Dry grasslands –81.0%; E7 Sparsely wooded grasslands – 5.0%; F3 Temperate and mediterranean-montane scrub – 10.0%; G1 Broadleaved deciduous woodland – 4.0%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; F3.1 83 Temperate thickets and scrub. Land use: mowing/hay making (major), forestry – minor. Protected areas: same as proposed state botanical reserve “Ofrys” Threats: abandonment/reducion of land management – high, forestry (aforestaion) – low. General descripion. Semi-dry grasslands, natural deciduous woods and shrubs (Frangula alnus, Prunus spinosa, Crataegus spp.). Grasslands are dominated by Inula ensifolia, Carex humilis, Peucedanum cervaria, Brachypodium pinnatum. Other frequent species: Geranium sanguineum, Salvia pratensis, Filipendula vulgaris, Carex montana, Stachis recta, Trifolium medium, Cirsium pannonicum, Eryngium planum, Prunella grandilora, Thalictrum minus, Agrimonia eupatoria, Asperula cynanchica, Campanula sibirica, Teucrium chamaedrys. Botanical signiicance. The only populaion of Ophrys apifera in Ukraine outside the Crimea. Criterion C • E1.2 Perennial calcareous grassland and basic steppes (6210, *Important orchid site); area: 3.5 ha; trend: decreasing; area data quality: good; trend data quality: good. Size of populaion of Ophrys apifera: 30–100 individuals. Conservaion proposals. Do not allow expansion of trees and shrubs, mow grasslands, non-intensive grazing. Create a state botanical reserve. Include in Halytskyi naional nature park and Emerald Site “Halytskyi Naional Nature Park”. Literature 1. Данилик І.М., Борсукевич Л.М. Нове місцезнаходження Ophrys apifera Huds. (Orchidaceae) в Україні // Укр. ботан. журн. – 2011. – 68, № 1. – С. 58-64. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 912 с. Protected areas: includes regional preserve (zapovidne urochyshche) “Dubrovy” (10.0 ha), includes regional preserve (zapovidne urochyshche) “Mochar” (8.0 ha), includes proposed regional botanical reserve “Bushtynskyi Park Liodovykovoho Periodu”. Threats: water (drainage) – medium. General description. A complex of deciduous forests, swamps and wet meadows. Woods Dubrova are represented by moist acidophilous Quercus robur forests (with Agrosis canina, Betonica oicinalis, Betula pubescens, Carex brizoides (dom.), Crataegus monogyna s. l., Deschampsia cespitosa, Euonymus europaeus, Frangula alnus, Molinia caerulea (dom.), Malus sylvestris, Populus tremula, Swida sanguinea (Cornus sanguinea) and hygrophylous species that are typical of alder swamps), mesic species rich Quercus robur forests (with Anemone nemorosa, Anemone ranunculoides, Carex curvata, Clemais recta, Corylus avellana, Frangula alnus, Fraxinus excelsior, Lathyrus niger, Malus sylvestris, Melica unilora, Populus nigra, Potenilla alba, Prunus spinosa, Polygonatum mulilorum, Pulmonaria oicinalis, Ranunculus polyanthemos, Serratula inctoria, Vicia cassubica, Vinca minor and less oten Crocus banaicus, Pilosella auraniaca (Hieracium auraniacum), Muscari transsilvanicum, Phyteuma vagneri, Rosa gallica, Veratrum album), wet Alnus gluinosa woods (with Carex elongata, Carex riparia, Carex vesicaria, Galium palustre, Glyceria maxima, Iris pseudacorus, Lycopus europaeus, Lythrum salicaria, Rubus caesius, Salix cinerea, Solanum dulcamara, Stachys palustris). Former fens and bogs are replaced by Molinia caerulea abandoned pastures (predominantly) and Alopecurus pratensis hay meadows. Botanical significance. The area is important for conservaion of termophilous oak forests and hygrophilous deciduous forests. Criterion C • E3.5 Moist or wet oligotrophic grassland; area: 350 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.21 Riverine Fraxinus – Alnus woodland (*91E0), wet at high but not at low water; area: 100 ha; trend: stable; area data quality: medium; trend data quality: medium. R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Дуброва. Area: 762.0 ha. Altitude: 202–219 m. Latitude: 48°05’13” N (48.0869°). Longitude: 23°28’48” E (23.4800°). Administrative regions. Zakarpatska region: Tiachiv raion. Ownership: state, private (minor). Biogeographic regions: pannonian. Habitats. Level 1. C – 0.1%; D – 1.0%; E – 51.3%; G – 47.1%; H – 0.5%. Habitats. Level 2. C2 Surface running waters – 0.1%, D2 – Valley mires, poor fens and transition mires – 0.0%; D5 Sedge and reedbeds, normally without free-standing water – 1.0%; E3 Seasonally wet and wet grasslands – 51.3%; G1 Broadleaved deciduous woodland – 47.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. D2.3 Transition mires and quaking bogs; D5.2 Beds of large sedges normally without free-standing water; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.7 Thermophilous deciduous woodland; G1.8 Acidophilous Quercus-dominated woodland; H5.6 Trampled areas. Land use: forestry – minor, agriculture (animals) – minor; mowing/hay making – minor. 84 85 • G1.7 Thermophilous deciduous woodland (*91I0); area: 50 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Raise the groundwater table. Create a botanical reserve and an Emerald Site. Lemna trisulca, Myriophyllum vericillatum, Myriophllum spicatum, Potamogeton pecinatus (Stuckenia pecinata), Salvinia natans, Spirodela polyrrhiza, Trapa natans. In brackish water Dunaiski Plavni V.A. Onyshchenko Ukrainian name: Дунайські плавні. Transliteraion/Translaion variants: Danube Wetlands. Area: 43601.0 ha. Altitude: 0–13 m. Latitude: 45°23’40” N (45.3945°). Longitude: 29°41’00” E (29.6833°). Administrative regions. Odesa region: Kiliya raion; Territorial waters of Ukraine . Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 11.2%; C – 10.7%; D – 71.1%; E – 5.0%; F – 0.4%; G – 1.6%. Habitats. Level 2. A2 Littoral sediment – 0.1%; A5 Sublittoral sediment – 11.1%; C1 Surface standing waters – 3.6%; C2 Surface running waters – 2.3%; C3 Littoral zone of inland surface waterbodies – 4.8%; D5 Sedge and reedbeds, normally without free-standing water – 70.9%; D6 Inland saline and brackish marshes and reedbeds – 0.2%; E1 Dry grasslands – 0.2%; E3 Seasonally wet and wet grasslands – 1.5%; E6 Inland salt steppes – 3.3%; F9 Riverine and fen scrubs – 0.4%; G1 Broadleaved deciduous woodland – 0.4% G3 Coniferous woodland – 1.2%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; D6.1 Inland saltmarshes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E3.4 Moist or wet eutrophic and mesotrophic grassland; E6.2 Coninental inland salt steppes; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations. Land use: isheries/aquaculture – minor; forestry – 2%; nature conservation and research – 76%; mowing/hay making – minor; urban/industrial/transport – 1%. Protected areas: overlaps (about 35747 ha) with Danube Delta transboundary biosphere reserve and Emerald Site “Danube Biosphere Reserve” (about 35747 ha). Threats: forestry (aforestaion) – medium. General description. The Ukrainian part of the Danube delta. It includes branches of the river, large reed marsches, lakes, meadows, halophyic vegetaion, 1 km strip of the Black Sea, a sand ridge with pine plantaions and dry sand grasslands. The dominant vegetaion type is freshwater marshes. The main dominant is Phragmites australis (a frequent codominant is Schoenoplectus lacustris), other important dominants are Typha angusifolia, Carex acuiformis, Carex elata, Carex pseudocyperus. Freshwater aquaic vegetaion is usually dominanted by Ceratophyllum demersum, Hydrocharis morsus-ranae, Lemna minor, 86 in the sea and lagoons, Zostera marina, Zostera nolii (Nanozostera nolii), Ruppia mariima predominate. Halophyic vegetaion is represented by communiies of annuals Salicornia perennans, Suaeda prostrara, Halimione pedunculata and perennials Aeluropus litoralis, Bolboschoenus mariimus, Carex distans, Carex extensa, Juncus gerardii, Juncus mariimus, Puccinellia gigantea. Broadleaved forests are represented mainly by riverine Salix alba woods, both natural and ariicial. On the largest area of dry sands (about 640 ha), there are plantaions of Pinus pallasiana and grasslands dominated by Calamagrosis epigeios and Carex colchica. On the sea beach sand ridges, dominants are Artemisia arenaria, Leymus sabulosus, Secale sylvestre. Psammophyic communiies contain a narrow endemic species, Dianthus bessarabicus. 87 Botanical significance. This area is richest in aquaic vascular plant species in Ukraine. Criterion A • Aldrovanda vesiculosa L.; A(i), A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Carex secalina Wahlenb.; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Dianthus bessarabicus Klokov; A(iii); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. • Salvinia natans (L.) All.; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. • Trapa natans L.; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: medium. • Typha minima Funk; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • C1.224 Floaing Utricularia australis and Utricularia vulgaris colonies; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.225 Floaing Salvinia natans mats; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.226 Floating Aldrovanda vesiculosa communities; area: 0.1 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C1.3411 Ranunculus communities in shallow water; area: 1 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C2.34 Eutrophic vegetation of slow-flowing rivers; area: 50 ha; trend: stable; area data quality: poor; trend data quality: medium. • D5.2 Beds of large sedges normally without free-standing water; area: 400 ha; trend: unknown; area data quality: good; trend data quality: poor. • E6.2 Continental inland salt steppes; area: 1400 ha; trend: stable; area data quality: poor; trend data quality: poor. Conservaion proposals. Restore sand grasslands on the areas occupied by Pinus plantaions. Literature 1. Біорізноманітність Дунайського біосферного заповідника, збереження та управління / Гол. ред. Ю.Р. Шеляг-Сосонко. – К.: Інтерекоцентр, 1999. – 702 с. 2. Дворецький Т.В. Вплив викошування на рослинність засолених луків Дунайського біосферного заповідника (ДБЗ) // Укр. фітоцен. зб. – К., 1999. – Сер. С, вип. 1 (15). – С. 68–78. 3. Дубина Д.В., Жмуд О.І. БЗ Дунайський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 31–44. 4. Дубына Д.В., Шеляг-Сосонко Ю.Р. Плавни Причерноморья. – К.: Наук. думка, 1989. – 272 с. 5. Дубина Д.В., Шеляг-Сосонко Ю.Р., Жмуд О.І., Жмуд М.Є., Дворецький Т.В., Дзюба Т.П., Тимошенко П.А. Дунайський біосферний заповідник. Рослинний світ. – К.: Фітосоціоцентр, 2003. – 459 с. 6. Зеров К.К. Водная растительность Килийской дельты Дуная // Дунай и придунайские водоемы в пределах СССР. – Тр. Ин-та гидробиологии АН УССР. – 36. – 88 С. 37–48. 7. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 8. Шеляг-Сосонко Ю.Р., Дубына Д.В. Государственный заповедник “Дунайские плавни”. – К.: Наук. думка, 1984. – 286 с. Dzharylhach V.A. Onyshchenko, V.P. Kolomiychuk Ukrainian name: Джарилгач. Area: 10555.0 ha. Altitude: 0–3 m. Latitude: 46°02’09” N (46.0358°). Longitude: 32°52’48” E (32.8800°). Administrative regions. Kherson region: Skadovsk raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 63.0%; B – 0.8%; C – 1.0%; E – 34.5%; G – 0.4%; H – 0.3%. Habitats. Level 2. A2 Littoral sediment – 20.0%; A5 Sublittoral sediment – 43.0%; B1 Coastal dunes and sandy shores – 0.6%; B2 Coastal shingle – 0.2%; C1 Surface standing waters – 1.0%; E1 Dry grasslands – 31.5%; E2 Mesic grasslands – 1.0%; E6 – Inland salt steppes – 2.0%; G1 Broadleaved deciduous woodland – 0.4%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.3%. Futher habitat description. A2.5 Coastal saltmarshes and saline reedbeds; A5.2 Sublitoral sand; A5.4 Sublitoral mixed sediments; A5.5 Sublitoral macrophyte-dominated sediment; B1.1 Sand beach driftlines; B1.2 Sand beaches above the driftline; B1.3 Shifting coastal dunes; B1.4 Coastal stable dune grassland (grey dunes); B1.8 Moist and wet dune slacks; B2.1 Shingle beach driftlines; B2.2 Unvegetated mobile shingle beaches above the driftline; C1.5 Permanent inland saline and brackish lakes, ponds and pools; D6.2 Inland saline or 89 brackish species-poor helophyte beds normally without free-standing water; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E6.2 Coninental inland salt steppes; G1.C Highly ariicial broadleaved deciduous forestry plantations; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservation and research – 95%; forestry – minor, tourism/recreation – minor. Protected areas: includes Dzharylhatskyi Naional Nature Park (10000 ha) and Emerald Site “Dzharylhatskyi Naional Nature Park” (10000 ha), included in Ramsar Site “Karkinitska and Dzharylgatska Bays”. Threats: climate change/sea level rise – low, forestry (afforestation) – medium, natural events (spit erosion) – low. General description. The IPA includes Dzharylhach accumulaive island with adjacent areas of the Black Sea. The island is composed of sand and shells. Its southern bank is steeper, with low dunes (1–2 m). The nothern bank is very low, with numerous lagoons. A large part of the island is occupied by dry grasslands in complex with saltmarshes and saline lakes. Aquaic vegetaion. Dominants: Zostera nolii (Nanozostera nolii), Zostera marina, Ruppia cirrhoza, Zannichellia palustris, Zannicelia pedunculata, Potamogeton pecinatus (Stuckenia pecinata). Tall helophytes communiies. Dominants: Phragmites australis, Cladium mariscus. Sand beach dritline vegetaion. Dominants: Cakile maritima, Euphorbia peplis, Salsola soda (Soda inermis), Polygonum mariimum. Sand dunes vegetaion. Dominants: Leymus sabulosus, Crambe pontica. Typical species: Argusia sibirica, Artemisia arenaria, Asperula graveolens, Carex colchica, Centaurea majorovii, Centaurea odessana, Cynanchum acutum, Eryngium mariimum, Euphorbia seguierana, Lactuca tatarica, Polygonum mesembricum, Secale sylvestre. Halophyic vegetaion. Dominants: Aeluropus litoralis, Bolbochoenus mariimus, Elytrigia elongata, Juncus gerardii, Juncus mariimus, Limonium caspium, Limonium meyeri, Puccinellia distans, Puccinellia fominii, Salicornia perennans, Suaeda prostrata. Dry grasslands on sands and shells. Dominants: Carex colchica, Carex praecox, Centaurea majorovii, Cynodon dactylon, Ephedra distachya, Euphorbia seguierana, Festuca beckeri, Festuca valesiaca, Poa angusifolia, Poa bulbosa, Secale sylvestre, Sipa borysthenica, Sipa capillata. Typical species: Artemisia arenaria, Asperula setulosa, Centaurea odessana. Mesic grasslands. Dominants: Calamagrosts epigeios, Elytrigia repens, Festuca pratensis, Poa pratensis. Botanical significance. Important area for conservaion of sand grasslands, litoral vegetaion, mesic and wet halophyic vegetaion, vegetaion of salt waters. Criterion C • A2.5 Coastal saltmarshes and saline reedbeds; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: medium. • A5 Sublitoral sediment; area: 4500 ha; trend: stable; area data quality: good; trend data quality: good. • B1.3 Shifting coastal dunes; area: 20 ha; trend: stable; area data quality: medium; trend data quality: medium. • B1.4 Coastal stable dune grassland (grey dunes); area: 20 ha; trend: stable; area data quality: medium; trend data quality: medium. • E1.2 Perennial calcareous grassland and basic steppes; area: 1000 ha; trend: stable; area data quality: poor; trend data quality: medium. 90 Literature 1. Биоразнообразие Джарылгача: современное состояние и пути сохранения / Котенко Т.И., Ардамацкая Т.Б., Дубына Д.В. и др. / Науч. ред. Т.И. Котенко, Ю.Р. ШелягСосонко. – Вестн. зоологии. – 2000. – Спец. выпуск. – 240 с. 2. Дубина Д.В., Дзюба Т.П., Ємельянова С.М. НПП Джарилгацький // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 230–239. 3. Дубина Д.В., Дзюба Т.П. Фітоценотична різноманітність острова Джарилгач (Херсонська обл.) // Укр. ботан. журн. – 2005. – 62, № 2. – С. 128–142. 4. Дубина Д.В., Тимошенко П.А. Особливості флористичного різноманіття острова Джарилгач // Укр. ботан. журн. – 2004. – 61. № 3. – С. 61–72. Dzhohul I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Джогуль. Area: 263 ha. Altitude: 944–1185 m. Latitude: 47°48’35” N (47.8096°). Longitude: 25°06’14” E (25.1038°). Administrative regions. Chernivtsi region: Putyla raion. Ownership: state (major), private. Biogeographic regions: alpine. Habitats. Level 1: C – 0.1%, E – 74.4%, G – 25.0%, H – 0.5%. Habitats. Level 2: C2 Surface running waters – 0.1%, E1 Dry grasslands – 29.0%; E2 Mesic grasslands – 41.4%, E3 Seasonally wet and wet grasslands – 1.0%; E7 Sparsely wooded grasslands – 3.0%; G1 Broadleaved deciduous woodland – 10.0%; G3 Coniferous woodland – 15.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description: C2.2 Permanent non-tidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland; E2.1 Permanent mesotrophic pastures and aftermath-grazed meadows; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; H5.6 Trampled areas. Land use: agriculture (animals) – minor; forestry – minor; mowing/hay making – major. Protected areas: –. Threats: abandonment/reducion of land management – medium; agricultural intensification/expansion (grazing) – low. General description. A complex of grasslands with small Picea abies woods, Fagus sylvaica woods and sparse trees. Grasslands are dominated by Helictotrichon praeustum, Agrostis tenuis, Anthoxanthum odoratum, Luzula luzuloides, Sieglingia decumbens, Lerchenfeldia flexuosa with some presence of Arnica montana, Astrantia major, Botrychium lunaria, Campanula serrata, Arabidopsis arenosa (Cardaminopsis arenosa), Carex umbrosa, Carlina acaulis, Coeloglossum viride, Dianthus compactus, Euphorbia carniolica, Festuca pratensis, Gentiana asclepiadea, Gymnadenia conopsea, Hypochaeris uniflora (Achyrophorus uniflorus), Leucorchis albida, Lilium martagon, Listera ovata (Neoia ovata), Luzula 91 multiflora, Melampyrum saxosum, Potentilla aurea, Potentilla erecta, Pyrethrum clusii, Scorzonera rosea, Soldanella montana, Thesium alpinum, Thymus pulegioides, Traunsteinera globosa, Trifolium montanum, Trollius europaeus, Vaccinium myrtillus, Vaccinium vitisidaea, Viola declinata. – P. 169–187. 2. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. Dziurkach I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Дзюркач. Area: 25.3 ha. Altitude: 398–448 m. Latitude: 48°18’03” N (48.3008°). Longitude: 25°46’30” E (25.7748°). Administrative regions. Chernivtsi region: Kitsman raion. Ownership: state, private. Biogeographic regions: alpine, coninental. Habitats. Level 1: E – 59.0%, G – 39.5%, H – 1.5%. Habitats. Level 2: E2 Mesic grasslands – 56.0%; G1 Broadleaved deciduous woodland – 39.5%; E7 Sparsely wooded grasslands – 3.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.5%. Botanical significance. The area includes about 5% of naional populaion of narrow endemic species Nigritella carpaica (Gymnadenia carpatica). Another Criterion A species Campanula serrata is frequent here. A good example of species rich mountain meadows with signiicant constancies of several Orchidaceae species. Criterion A • Nigritella carpatica (Zapał.) Teppner, Klein et Zagulski (Gymnadenia carpatica (Zapał.) Teppner et Klein); A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Campanula serrata (Kit. ex Schult.) Hendrych; A(ii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Maintain mowing of the meadows. Create a state botanical reserve and an Emerald Site. Literature 1. Teppner H., Klein Е., Drescher A., Zahulskij М. Nigritella carpatica (Orchidaceae) – ein Reliktendemit der Ost-Karpaten // Phyton. Annales rei botanicae. – 1994. – 34, № 2. 92 Futher habitat description: E2.2 Low and medium alitude hay meadows; G1.6 Fagus woodland; H5.6 Trampled areas. Land use: forestry – minor; mowing/hay making – major. Protected areas: included in Chernivetskyi regional landscape park and Emerald Site 93 “Chernivetskyi regional landscape park”. Threats: –. General description. Complex of species-rich hay meadows with small areas of broadleaved woods and sparse trees. Meadows are dominated by Arrhenatherum elatior, Anthoxanthum odoratum, Brachypodium pinnatum, Briza media, Dactylis glomerata, Cynosurus cristatus, Festuca pratensis, Festuca rubra, Molinia caerulea agg, Trisetum flavescens. Other frequent species: Adenophora liliifolia, Centaurea jacea, Crepis sibirica, Ferulago sylvatica, Filipendula vulgaris, Galium verum, Laserpitium latifolium, Leucanthemum vulgare, Pedicularis exaltata, Peucedanum oreoselinum, Pteridium aquilinum, Pyrethrum corymbosum, Serratula tinctoria, Trifolium montanum, Trifolium pannonicum, Veratrum nigrum. Botanical significance. Important area for Adenophora liliifolia. Extreme species rich grassland. Criterion A • Adenophora liliifolia; A(ii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Literature 1. Roleček J., Čornej I.I., Tokarjuk A.I. Understanding the extreme species richness of semi-dry grasslands in east-central Europe: a comparaive approach // Preslia. – 2014. – 86: 1–XX. – P. 13–34. Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: forestry – minor, mowing/hay making – minor, nature conservation and research – major. Protected areas: includes Gorgany nature reserve (5344.2 ha), overlaps (about 3429 ha) with Karparskyi naional nature park, includes Emerald Site “Gorgany Nature Reserve” (5344.2 ha), overlaps (about 3429 ha) with Emerald Site “Carpathian Naional Nature Park”. Threats: climate change/sea level rise – low, development (recreaion/tourism) – low Gorgany V.A. Onyshchenko Ukrainian name: Горгани. Transliteraion/Translaion variants: Horhany mountains. Area: 9217.0 ha. Altitude: 690–1755 m. Latitude: 48°24’11” N (48.4030°). Longitude: 24°25’03” E (24.4176°). Administrative regions. Ivano-Frankivsk region: Nadvirna raion, Yaremche city. Ownership: state (major), private. Biogeographic regions: alpine. Habitats. Level 1. C – 0.2%; E – 1.3%; F – 5.3%; G – 89.7%; H – 3.5%. Habitats. Level 2. C2 Surface running waters – 0.2%; E1 Dry grasslands – 0.4%; E2 Mesic grasslands – 0.3%; E4 Alpine and subalpine grasslands stands – 0.5%; E5 Woodland fringes and clearings and tall forb stands – 0.1%; F2 Arctic, alpine and subalpine scrub – 5.3%; G1 Broadleaved deciduous woodland – 2.0%; G3 Coniferous woodland – 62.7%; G4 Mixed deciduous and coniferous woodland – 25.0%; H2 Screes – 3.3%; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E4.2 Moss and lichen dominated mountain summits, ridges and exposed slopes; E4.3 Acid alpine and subalpine grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 94 General description. The major vegetaion type is Picea abies forest (pure or co-dominated by Abies alba, Pinus cembra or Pinus sylvestris). Dominants of the herb layer are Calamagrosis villosa, Luzula luzuloides, Vaccinium myrillus. Typical species of the herb layer are Dryopteris dilatata, Homogyne alpina, Luzula sylvaica, Oxalis acetosella, Vaccinium viisidaea. The moss layer is formed by Polytrichum formosum, Pleurozium schreberi, Dicranum scoparium, Bazzania trilobata, Leucobryum juniperoides. 10–15% of the coniferous forest is the primeval forest. A large area is covered by mixed Fagus sylvaica – Abies alba – Picea abies forests. Its herb layer consists of Anemone nemorosa, Dentaria glandulosa, Dryopteris ilix-mas, Euphorbia amygdaloides, Galium odoratum, Glechoma hirsuta, Mercurialis perennis, 95 Oxalis acetosella, Polygonatum vericillatum, Senecio ovatus, Symphytum cordatum, Viola reichenbachiana. On the mountain tops, there are large areas of unvegetated coarse sandstone screes and Pinus mugo thickets. Besides there are communities of Duschekia alnobetula (Alnus alnobetula) and Juniperus sibirica. Botanical significance. Important area for mountain Picea abies forests and Carpathian Pinus cembra forests. Criterion C • F2.46 (*4070) Carpathian Pinus mugo scrub; area: 400 ha; trend: stable; area data quality: medium; trend data quality: poor. • G3.1B Alpine and Carpathian subalpine Picea forests; area: 5800 ha; trend: stable; area data quality: medium; trend data quality: medium. • G3.25 Carpathian Larix and Pinus cembra forests; area: 90 ha; trend: decreasing; area data quality: medium; trend data quality: medium. • H2.3 Temperate-montane acid siliceous screes; area: 300 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1.Берко Й.М. Фітоценотичний нарис смерекових лісів (Piceeta abietis) на Горганах // Укр. ботан. журн. – 1970. – 28, № 5. – С. 608–613. 2.Клімук Ю.В., Міскевич У.Д., Якушенко Д.М., Чорней І.І., Буджак В.В., Нипорко С.О., Шпільчак М.Б., Чернявський М.В., Токарюк А.І. та ін. Природний заповідник “Горгани”. Рослинний світ. – Природно-заповідні території України. Рослинний світ. Вип. 6. – К.: Фітосоціоцентр, 2006. – 400 с. 3.Стойко С.М., Третяк П.Р., Бойчук І.І. Сосна кедрова (Pinus cembra L.) на верхній межі лісу у Ґорґанах: хорологія, екологія, фенологія // Науковий вісник ДЛГУ: Дослідження, охорона та збагачення біорізноманіття. – Львів: Вид-во ЛДГУ, 1999. – Вип. 99. – С. 173–179. 4.Чорней І.І., Токарюк І.І., Буджак В.В. ПЗ Горгани // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 94–101. alpine and subalpine scrub – 16.0%; G1 Broadleaved deciduous woodland – 0.3%; G3 Coniferous woodland – 78.9%; G4 Mixed deciduous and coniferous woodland – 0.1%; H2 Screes – 4.0%; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Grofa V.A. Onyshchenko Ukrainian name: Грофа. Transliteraion/Translaion variants: Hrofa Mount. Area: 5610.0 ha. Altitude: 815–1748 m. Latitude: 48°35’19” N (48.5885°). Longitude: 23°55’46” E (23.9293°). Administrative regions. Ivano-Frankivsk region: Rozhniaiv raion (major); Zakarpatska region: Tiachiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.1%; E – 0.3%; F – 16.0%; G – 79.3%; H – 4.3%. Habitats. Level 2. C2 Surface running waters – 0.1%; E1 Dry grasslands – 0.3%; F2 Arctic, 96 Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.6 Fagus woodland; G3.1 Abies and 97 Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: forestry – major; nature conservation and research – major, tourism/recreaion – minor. Protected areas: overlaps (about 2450 ha) with Grofa state landscape reserve, overlaps (5375 ha) with Emerald Site “Dolynsko-Rozhniatynskyi”. Threats: forestry (intensiied forest management) – low. General description. The major vegetaion type is the mountain Picea abies forest on acid soil. A part of spruce forests (>500 ha) has some admixture of Pinus cembra. Besides there are large areas of Pinus mugo scrub and coarse sandtone screes in the subalpine belt. Botanical significance. Important area for mountain Picea abies forests. Criterion C • F2.46 (*4070) Carpathian Pinus mugo scrub; area: 850 ha; trend: stable; area data quality: medium; trend data quality: poor. • G3.1B Alpine and Carpathian subalpine Picea forests; area: 4450 ha; trend: stable; area data quality: good; trend data quality: poor. Literature 1. Природно-заповідні території та об’єкти Івано-Франківщини. – Івано-Франківськ, 2000. – 272 с. Perennial calcareous grassland and basic steppes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E2.2 Low and medium alitude Hadiatski Luky N.O. Stetsiuk, V.A. Onyshchenko Ukrainian name: Гадяцькі луки. Transliteraion/Translaion variants: Hadiatski Meadows, Hadiach Meadows, Gadiach Meadows. Area: 15123 ha. Altitude: 93–108 m. Latitude: 50°18’40” N (50.3111°). Longitude: 34°02’04” E (34.0343°). Administrative regions. Poltava region: Hadiach raion (major), Myrhorod raion; Sumy region: Lebedyn raion. Ownership: state (major), private. Biogeographic regions: coninental. Habitats. Level 1. C – 2.5%; D – 5.0%; E – 65.6%; F – 0.2%; G – 26.7%. Habitats. Level 2. C1 Surface standing waters – 0.5%; C2 Surface running waters – 1.9%; C3 Littoral zone of inland surface waterbodies – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 5.0%; E1 Dry grasslands – 1.0%; E2 Mesic grasslands – 46.5%; E3 Seasonally wet and wet grasslands – 16.1%; E6 Salt steppes – 2.0%; F9 Riverine and fen scrubs – 0.2%; G1 Broadleaved deciduous woodland – 25.7%; G3 Coniferous woodland – 0.7%; G4 Mixed deciduous and coniferous woodland – 0.3%. Futher habitat descripion. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.5 Periodically inundated shores with pioneer and ephemeral vegetation; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.2 98 hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E6.2 Coninental inland salt steppes; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.3 Mediterranean riparian woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – 99 acidophilous Quercus woodland. Land use: forestry – 30%; mowing/hay making – major, nature conservation and research – major. Protected areas: overlaps (about 9437 ha) with Hadiatskyi regional landscape park, includes Pisotsko-Konkove regional landscape reserve (204 ha), includes Ternovyi Kushch regional reserve (303 ha), includes Velyky Lis regional botanical reserve (182 ha), includes Zozulyntsevi Luky regional botanical reserve (45 ha), overlaps (about 9437 ha) with Emerald Site “Hadiatskyi Regional Landscape Park”. Threats: abandonment/reducion of land management – low; agricultural intensiicaion/ expansion (general) – low; forestry (intensiied forest management) – low; development (recreaion/tourism) – low. General description. A part of the loodplain of the Psel river. The pastures are dominated by Poa pratensis, Festuca pratensis, Dactylis glomerata, Elytrigia repens, Phleum pretense, Bromopsis inermis, Agrosis gigantea, Lolium perrene, Calamogrosis epigeios. Their constant species are Trifolium repens, T. pratens, Medicago lupulina, M. falcata, Vicia cracca, V. villosa, V. tetrasperma, V. grandilora, Plantago media, Ranunculus polyanthemos, R. acris, Rumex thyrsilorus, Equisetum pratense, Glechoma hederacea, Lysimachia nummulara, Prunella vulgaris, Potenilla anserina. The largest area is occupied by mesic hay meadows. They are dominated by Poa pratensis, Festuca pratensis, Alopecurus pratensis, Dactylis glomerata, Elytrigia repens, Arhrenantherum elaius. Other species of high constancy are Bromopsis inermis, Plantago lanceolata, Potenilla argentea, Galium ruthenicum, Cerasium holosteoides, Medicago falcata, Psammophiliella muralis, Achillea submillefolium, Echium vulgare, Verbascum lychniis, Veronica spicata, Hypericum perforatum, Centaurium erythraea, Silene viscaria (Steris viscaria, Viscaria viscosa), Trifolium alpestre, Fragaria viridis. In drier habitats, there dominate Festuca rubra, Festuca pseudovinae, Festuca beckeri, Festuca valesiaca, Poa angusifolia, Anthoxanthum odoratum. In the moist grasslands, there prevail Poa palustris, Beckmannia eruciformis, Agrosis stolonifera, in saline grasslands – Festuca orientalis, Alopecurus arundinaceae, Carex distans, Juncus gerardii, Eleocharis uniglumis, Plantago salsa, Boulboschoenus mariimus. Sedge and reedbeds are dominated by Phragmites australis, Typha angusifolia, T. laifolia, Glyceria maxima, G. luitans, Carex acuta, C. acuiformis, C. riparia, C. elata, Schoenoplectus lacustris, Phalaroides arundinacea, Sium laifolium. Main aquaic dominants are Hydrocharis morsus-ranae, Spirodella polyrhyza, Lemna minor, L. trisulca, Batrachium aquaile (Ranunculus aquailis), B. rionii (Ranunculus rionii), Nuphar lutea, Ceratophyllum demersum, Potamogeton natans, P. crispus, P. perfoliatus, P. pecinatum (Stuckenia pecinata), P. lucens. Mesic deciduous forests on the slopes of the valley and in the loodplain are dominated by Quercus robur, Tilia cordata, Acer platanoides, Acer campestre. Dominants of the shrub layer are Corylus avellana (major), Euonymus europaeus, E. verrucosus, Frangula alnus (in moist places), dominants of the herb layer – Stellaria holostea, Aegopodium podagraria, Convallaria majalis. Forests dominanted by Alnus gluinosa have the herb layer consising mainly of Urica galeopsifolia, Eupatorium cannabinum, Galium aparine, Carex acuiformis. Besides there are forests dominated by Populus nigra, P. tremula, P. alba. Their typical species are Aegopodium podagraria, Convallaria majalis, Frangula alnus, Glechoma hederacea, Poa palustris, Rubus caesius, Sambucus nigra, Urica dioica. Botanical significance. Important area for mesic loodplain hay meadows. Criterion C • E2.2 Low and medium alitude hay meadows; area: 6000 ha; trend: stable; area data quality: medium; trend data quality: medium. 100 Literature 1. Стецюк Н.А., Ханнанова О.Р. Флоросозологическая характеристика проектированного регионального ландшафтного парка “Гадячский” (Украина, Полтавская область) // Структурно-функциональная организация и динамика растительного покрова: материалы Всероссийской науч.-практ. конф. с международным участием. – Самара, 2011. – С. 56–59. 2. Ханнанова О.Р. Раритетна флора регіонального ландшафтного парку “Гадяцький” (Полтавська область)” // Актуальні проблеми ботаніки та екології: мaт-ли Міжнарод. конф. молодих учених. – Умань, 2014. – С. 68–69. Halitsynove V.P. Kolomiychuk Ukrainian name: Галіцинове. Area: 7.4 ha. Altitude: 8–13 m. Latitude: 46°48’10” N (46.8028°). Longitude: 31°57’25” E (31.9569°). Administrative regions. Mykolaiv region: Vitovka (Zhovtnevyi) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 97.0%; H – 2.0%; J – 1.0%. Habitats. Level 2. E1 Dry grasslands – 97.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 2.0%; J4 Transport networks & other contructed hard-surfaced areas – 1.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; H5.6 Trampled areas. Land use: nature conservation and research – major. Protected areas: overlaps (about 7 ha) with Starohalicynivska regional botanical nature monument. Threats: abandonment/reducion of land management – low, burning of vegetaion – low. General description. Grassland on the sand terrace of the Southern Bug (Buh) river. Dominant species are Artemisia marschalliana, Thymus pallasianum, Secale sylvestre. Other frequent species are Carex colchica, Chondrilla juncea, Euphorbia seguieriana, Rumex acetosella, Jacobaea borysthenica (Senecio borysthenicus), Seseli tortuosum. Populaion of Centaurea protomargaritacea occupies minimum 4 ha. Density of the species is between 2 and 30 specimens per 100 m2. Botanical significance. Important area for the narrow endemic species Centaurea protomargaritacea (one of two localiies). Criterion A • Centaurea protomargaritacea Klokov; A(iii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals: Do not allow aforestaion. Change the status of regional botanical nature monument to state botanical nature monument. Literature 1. Коломієць Г.В. Перлинні волошки секції Pseudophalolepis Klok. ряду Margaritacea 101 Holohirskyi Lis V.A. Onyshchenko Ukrainian name: Гологірський ліс. Transliteraion/Translaion variants: Holohirsky Forest, Gologirskyi Forest. Area: 609.0 ha. Klok. Питання систематики та охорони // Укр. фітоценологічний зб. – Вип. 1–2 (12–13). – К.: Фітосоціоцентр, 1999. – С. 165–169. 2.Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. (Centaurea L.) // Укр. ботан. журн. – 1991. – 48, № 3. – С. 78 – 80. 3.Крицька Л.І., Деркач О.М. Волошка первинноперлинна Centaurea protomargaritacea Klokov (C. margaritacea Ten. subsp. protomargaritacea (Klokov) Dostál) / Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 308. 4.Перлини піщаної флори у пониззях Південного Бугу та Інгулу. Cерія: Збереження біорізноманіття в Приморсько-степовому екокоридорі / Під ред. Г.В. Коломієць. – К.: Громадська організація “Веселий Дельфін”, 2008. – 60 c. 102 Altitude: 277–461 m. Latitude: 49°46'10" N (49.7693°). Longitude: 24°39'40" E (24.6610°). Administrative regions. Lviv region: Zolochiv raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 0.2%; G – 98.8%; H – 1.0%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 94.5%; G4 Mixed deciduous and coniferous woodland – 4.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion. G1.6 Fagus woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – 100%. Protected areas: included in Pivnichne Podillia naional nature park, includes state complex nature monument "Hora Vapniarka" (309.8 ha), includes regional preserve "Lis Pid Trudovachem" (33 ha), includes regional geological nature monument "Velykyi Kamin" (0.03 ha), included in Emerald Site "Pivnichne Podillia". 103 Threats: –. General description. Hills covered by broadleaved forest. A large area is occupied by a species-rich Fagus sylvaica forest on calcium rich soil. Botanical significance. Important area for limestone beech forest. Criterion C • G1.66 Medio-European limestone Fagus forests (*9150); area: 200 ha; trend: stable; area data quality: poor; trend data quality: medium. Homilshanskyi Lis V.A. Onyshchenko Ukrainian name: Гомільшанський ліс. Transliteraion/Translaion variants: Homilshansky Forest, Gomil'shansky Forest. Area: 5450.0 ha. Altitude: 80–200 m. Latitude: 49°35'14" N (49.5872°). Longitude: 36°18'28" E (36.3076°). 104 Administrative regions. Kharkiv region: Zmiiv raion. Ownership: state . Biogeographic regions: steppic. Habitats. Level 1. C – 1.0%; E – 0.7%; G – 97.3%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.3%; C2 Surface running waters – 0.7%; E2 Mesic grasslands – 0.5%; E3 Seasonally wet and wet grasslands – 0.2%; G1 Broadleaved deciduous woodland – 97.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: mowing/hay making – minor; forestry – 98%; nature conservaion and research – 100%; tourism/recreaion – minor. Protected areas: included in Homilshanski Lisy naional nature park and Emerald Site "Gomilshanski Lisy Naional Nature Park". Threats: forestry (intensiied forest management) – low. General description. The major vegetaion type is the mesic broadleaved forest dominated by Quercus robur. Other important species of the tree layer are Fraxinus excelsior, Tilia cordata, Acer campestre, Acer platanoides. In the herb layer, there prevail Carex pilosa, Stellaria holostea, Aegopodium podagraria, someimes Asarum europaeum, Mercurialis perennis, Convallaria majalis, Galium odoratum. In spring there dominate Corydalis marschalliana, Corydalis solida, Anemone ranunculoides, Ficaria verna, Scilla siberica, someimes Allium ursinum, Tulipa quercetorum. Other species of high constancy are Corylus avellana, Euonymus europaeus, Euonymus verrucosus, Gagea lutea, Lathyrus vernus, Polygonatum mulilorum, Pulmonaria obscura, Ulmus glabra, Viola mirabilis, Viola odorata. The forest belongs to the zones of strict protecion and regulated recreaion of the naional nature park "Homilshanski Lisy". The western part of the IPA is the loodplain of the Siverskyi Donets river. Vegetaion of this area is Quercus robur forests, Alnus gluinosa forests, meadows and aquaic vegetaion. Botanical significance. Important for conservaion of mesic deciduous forests. Criterion C • G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; area: 5300 ha; trend: stable; area data quality: good; trend data quality: good. Literature 1. Байрак О.М. Лишайники Гомольшанського державного природного парку // Укр. ботан. журн. – 1987. – 44, № 4. – С. 38–42. 2. Вовк О.Г., Клімов О.В., Філатова О.В., Тверетінова В.В. Ботанічна характеристика проектованого національного природного парку "Гомільшанські ліси" // Біологія та валеологія: Зб. наук. праць. – Харків: ХДПУ, 2000. – Вип. 2. – С. 167–178. 3. Горелова Л.Н. Национальный природный парк "Гомольшанский" // Характеристика основних заповідних територій Харківської області. – Харків: Мін-во освіти і науки України, 2004. – С. 14–23. 4. Горелова Л.Н., Алехин А.А., Друлева И.В., Гамуля Ю.Г. Редкие и исчезающие растения национального природного парка "Гомольшанские леса". – Харьков: Видавничий центр ХНУ ім. В.Н. Каразіна, 2007. – 137 с. 105 5. Горєлова Л.М., Альохін О.О., Комариста В.П., Гамуля Ю.Г. Лікарські рослини Національного природного парку "Гомільшанські ліси". – Харків: Видавничий центр ХНУ ім. В.Н. Каразіна, 2006. – 122 с. 6. Леонтьев Д.В. Видовой состав миксомицетов (Myxomycota) национального природного парка "Гомольшанские леса" (Украина) // Микол. и фитопатол. – 2006. – 40, вып. 2. – С. 101–107. 7. Леонтьев Д.В. Фитоценотические связи миксомицетов (Myxomycetes) в Национальном природном парке "Гомольшанские леса" (Украина) // Экология. – 2007. – № 2. – C. 1–3. 8. Перспективная сеть заповедных объектов Украины / Ю.Р. Шеляг-Сосонко, С.М. Стойко, Я.П. Дидух и др. – К.: Наук. думка, 1987. – С. 128–132. 9. Саідахмедова Н.Б. Проблеми збереження фіторізноманіття в НПП "Гомільшанські ліси" та шляхи їх вирішення // Каразінські прирородознавчі студії: Мат-ли наук. конф. з міжнар. участю, присвяченої 100-річчю з дня народження Ю.М. Прокудіна і О.М. Матвієнко – професорів Харківського університету. – Харків: Харк. нац. ун-т ім. В.Н. Каразіна, 2011. – С. 68–71. 10. Саідахмедова Н.Б., Філатова О.В., Клімов О.В., Прилуцький О.В., Акулов О.Ю., Біатов А.П. НПП Гомільшанські ліси // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 152–175. 11. Сивоконь О.В. Гастероїдні базидіоміцети Національного природного парку "Гомільшанські ліси" // Заповідна справа в Україні. – 2008. – Т. 14, № 2. – С. 56–62. "Podilski Tovtry Naional Nature Park". Threats: agricultural intensification/expansion (grazing) – low, development (recreaion/ tourism) – low. Horaivka L.H. Lubinska, L.T. Horbnyak Ukrainian name: Гораївка. Area: 11.4 ha. Altitude: 122–244 m. Latitude: 48°34'57" N (48.5825°). Longitude: 26°59'55" E (26.9985°). Administrative regions. Kmelnytskyi region: Kamianets-Podilskyi raion. Ownership: state (major), private. Biogeographic regions: coninental. Habitats. Level 1. E – 22.0%; F – 4.5%; G – 68.2%; H – 5.3%. Habitats. Level 2. E1 Dry grasslands – 22.0%; F3 Temperate and mediterranean-montane scrub – 4.5%; G1 Broadleaved deciduous woodland – 68.2%; H2 Screes – 4.0%; H3 Inland clifs, rock pavements and outcrops – 1.3%. Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs. Land use: agriculture (animals) – minor, forestry – minor, nature conservation and research – major, tourism/recreaion – minor. Protected areas: included in Podilski Tovtry naional nature park, included in Emerald Site General description. The steep slope of the Dnister valley with deciduous forests, dry grasslands, shrub vegetaion, calcareous rocks and screes. Steppes are dominated by Sipa сapillata, Festuca valesiaca, Elytrigia intermedia, Sesleria heuleriana. Typical species are Leontodon hispidus, Pulsailla grandis, Pulsailla pratenis, Verbascum nigrum. On rocks there are Allium podolicum, Asperula cynanchica, Aurinia saxailis, Melica transsylvanica, Potenilla arenaria, Salvia vericillata, Sempervivum ruthenicum, Teucrium chamaedrys, Thymus moldavicus, Veronica incana. The area belongs to the zone of strict protecion of naional nature park "Podiliski Tovtry". Botanical significance. One of the best populaions of Pulsailla grandis in Ukraine. Criterion A • Pulsailla grandis Wend.; A(ii); abundance: occasional (1000 individuals, including 300 generaive ones); trend: unknown; species data quality: good; trend data quality: poor. 106 107 Administrative regions. Ternopil region: Pidvolochysk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 98.8%; F – 1.0%; H – 0.2%. Habitats. Level 2. E1 Dry grasslands – 90.0%; E2 Mesic grasslands – 8.8%; F3 Temperate and mediterranean-montane scrub – 1.0%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 0.1% Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.2 Low and medium alitude hay meadows; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: nature conservation and research – 100%. Protected areas: included in Medobory nature reserve, included in Emerald Site "Medobory Nature Reserve". Threats: abandonment/reducion of land management – medium, burning of vegetaion – low. General description. Three hills with limestone outcrops. The major vegetaion type is the meadow steppe dominated by Poa angusifolia, Festuca valesiaca s.l., Carex humilis. Someimes there dominate Calamagrosis epigeios, Brachypodium pinnatum, Festuca pratensis. Species of high constancy are Achillea millefolium s.l., Acinos arvensis, Artemisia absinthium, Cerasium arvense, Eryngium planum, Filipendula vulgaris, Fragaria viridis, Galium verum, Hypericum perforatum, Koeleria cristata, Pedicularis kaufmannii, Plantago media, Pimpinella saxifraga, Primula veris, Polygala comosa, Potenilla argentea, Ranunculus polyanthemos, Salvia pratensis s.l. (Salvia dumetorum), Salvia vericillata, Scabiosa ochroleuca, Jacobaea vulgaris (Senecio jacobaea), Seseli annuum, Thymus marschallianus, Veronica incana, Viola hirta. Typical species on the outcrops are Asperula cynanchica, Allium lusitanicum s.l. (Allium montanum auct.), Aurinia saxailis, Arabidopsis arenosa (Cardaminopsis arenosa), Galium campanulatum, Poa compressa, Potenilla incana, Sedum acre, Torella tortuosa, Tortula ruralis. Botanical significance. The largest populaion of Dracocephalum austriacum in Ukraine, probably one of two largest populaions of Pulsailla grandis in Ukraine. Important area for conservaion of Carlina cirsioides. Criterion A • Carlina cirsioides Klokov; A(iv); abundance: occasional (500 individuals); trend: stable; species data quality: good; trend data quality: medium. • Dracocephalum austriacum L.; A(ii); abundance: frequent (3500 individuals); trend: stable; species data quality: good; trend data quality: medium. • Pulsailla grandis Wender.; A(ii); abundance: frequent (15000 individuals); trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals: Mow a part of the grasslands. Literature 1. Szafer W. Geobotaniczne stosunki Miodoborόw Galicyjskich // Rozpr. Wydz. Matemat.-Przyrod. Akad. Umiejętności. – 1910. – Ser. 3, Dz. B, T. 10. – S. 63–172. 2. Данилків І.С., Рабик І.В. Мохоподібні (Bryophytes) природного заповідника "Медобори" // Чорноморський ботан. журн. – 2007. – 3, № 1. – С. 85–99. 3. Кондратюк С.Я. Лишайники заповідника "Медобори" // Укр. ботан. журн. – 1995. – 52, № 1. – С. 141–144. 4. Кондратюк С.Я., Коломієць І.В. Нові для України види лишайників та ліхенофільних грибів заповідника "Медобори" // Укр. ботан. журн. – 1997. – 54, № 1. – С. 42–47. 5. Оліяр Г. І. Рослини Червоної книги України в природному заповіднику "Медобори" // Заповідна справа в Україні. – 1995. – Т. 1. – С. 11–12. 6. Оліяр Г. І. Фітораритети природного заповідника "Медобори" з філією "Кременецькі гори" в міжнародних червоних списках // Природно-заповідний фонд України – минуле, сьогодення, майбутнє. Матеріали міжнародної науковопрактичної конференції, присвяченої 20-річчю природного заповідника "Медобори" (смт. Гримайлів, 26–28 травня 2010 р.) – Тернопіль: Підручники і посібники, 2010. – С. 460–464. 108 109 Horodnytski Tovtry Ukrainian name: Городницькі товтри. Transliteraion/Translaion variants: Gorodnytski Tovtry. Area: 54.0 ha. Altitude: 343–389 m. Latitude: 49°24'12" N (49.4032°). Longitude: 26°04'09" E (26.0691°). H.I. Oliiar 7. Онищенко В.А. Рослинність карбонатних відслонень природного заповідника "Медобори" // Укр. фітоцен. зб. – Сер. A. – 2001. – 1 (17). – С. 86–104. 8. Онищенко В.А., Оліяр Г.І. ПЗ Медобори // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 254–276. 9. Смеречинская Т. А. Закономерности распространения лишайников по фитоценозам природного заповедника "Медоборы" // Заповідна справа в Україні. – 2005. – Т. 11, Випуск 1. – С. 9–15. Horodnytskyi Lis V.A. Onyshchenko Ukrainian name: Городницький ліс. Transliteraion/Translaion variants: Horodnytskyi Forest, Gorodnytskiy Forest. Latitude: 50°50'45" N (50.8460°). Longitude: 27°18'19" E (27.3051°). Administrative regions. Zhytomyr region: Novohrad-Volynskyi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 0.1%; E – 0.2%; G – 99.2%; H – 0.5%. Habitats. Level 2. D2 Valley mires, poor fens and transition mires – 0.1%; E3 Seasonally wet and wet grasslands – 0.1%; G1 Broadleaved deciduous woodland – 28%; G3 Coniferous woodland – 10.0%; G4 Mixed deciduous and coniferous woodland – 61.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. D2.3 Transiion mires and quaking bogs; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H5.6 Trampled areas. Land use: nature conservation and research – 100%; forestry – major. Protected areas: same as Horodnytskyi state botanical reserve, included in Emerald Site "Horodnytskyi". Threats: – General description. Major vegetaion types are mixed Pinus sylvestris – Quercus robur forest, acidophilous Quercus robur forest, acidophilous Pinus sylvestris forest. The largest area is occupied by mixed pine-oak forest with dominance of Rhododendron luteum in the shrub layer and Vaccinium myrillus in the layer of dwarf shrubs and herbs. In the lower layers of oak forest, there dominate Corylus avellana, Rhododendron luteum, Carex brizoides, Vaccinium myrillus. Pine forest is dominated by Vaccinium myrillus and Pleurozium schreberi. Besides there are small areas of swamped pine woods with Eriophorum vaginatum, Vaccinium uliginosum, Sphagnum sp. and transiion mires dominated by Carex lasiocarpa, Carex rostrata, Sphagnum sp. Botanical significance. A good example of oak and mixed pine-oak acidophilous forests with Rhododendron luteum. Criterion C • G1.8 Acidophilous Quercus-dominated woodland; area: 90 ha (together with mixed oak-pine forests – 300 ha); trend: stable; area data quality: good; trend data quality: medium. Literature 1. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 215 с. 2. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Area: 343 ha. Altitude: 195–202 m. 110 111 Habitats. Level 1. E – 5.0%; F – 75.5%; G – 19.0%; H – 0.5%. Habitats. Level 2. E1 Dry grasslands – 5.0%; F3 Temperate and mediterranean-montane scrub – 75.5%; G1 Broadleaved deciduous woodland – 19.0%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 0.4%. Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: nature conservation and research – 100%; tourism/recreaion – minor. Protected areas: included in Medobory nature reserve, included in Emerald Site "Medobory Nature Reserve". Threats: abandonment/reducion of land management – medium. General description. A hill with limestone outcrops. Major vegetaion type is the shrubs dominated by Crataegus leiomonogyna, Euonymus europaeus, Swida sanguinea (Cornus sanguinea). On the northern slope, there is a small area of the broadleaved wood with a dense shrub layer. On the ridge and in upper part of the southern slope, there is the steppe vegetaion in complex with limestone outcrops. The stepe vegetaion is dominated by Carex humilis, Dictamnus albus, Anthericum ramosum, Sipa pennata. Typical species on the outcrops are Asperula cynanchica, Aurinia saxailis, Centaurea stoebe, Festuca valesiaca, Galium campanulatum, Koeleria cristata, Melica transsilvanica, Potenilla incana, Sedum acre, Seseli libanois, Thymus dimorphus, Veronica incana. Main threat is overgrowing by shrubs and trees. Management includes clearing of shrubs and trees on a part of the area. Botanical significance. Important area for conservaion of Dracocephalum austriacum and Schivereckia podolica (Draba podolica). Criterion A • Dracocephalum austriacum L.; A(ii); abundance: occasional (230 individuals); trend: luctuaing; species data quality: good; trend data quality: good. • Schivereckia podolica (Besser) Andrz. ex DC. (Draba podolica (Besser) Rupr.); A(ii); abundance: frequent (3000 individuals); trend: decreasing; species data quality: good; trend data quality: medium. Conservaion proposals: Do not allow natural aforestaion. Literature 1. Szafer W. Geobotaniczne stosunki Miodoborόw Galicyjskich // Rozpr. Wydz. Matemat.-Przyrod. Akad. Umiejętności. – 1910. – Ser. 3, Dz. B, T. 10. – S. 63–172. 2. Данилків І.С., Рабик І.В. Мохоподібні (Bryophytes) природного заповідника "Медобори" // Чорноморський ботан. журн. – 2007. – 3, № 1. – С. 85–99. 3. Кондратюк С.Я. Лишайники заповідника "Медобори" // Укр. ботан. журн. – 1995. – 52, № 1. – С. 141–144. 4. Кондратюк С.Я., Коломієць І.В. Нові для України види лишайників та ліхенофільних грибів заповідника "Медобори" // Укр. ботан. журн. – 1997. – 54, № 1. – С. 42–47. 5. Оліяр Г.І. Зміни у флорі природного заповідника "Медобори" за минуле сторіччя // Роль природно-заповідних територій Західного Поділля та Юри Ойцовської у збереженні біологічного та ландшафтного різноманіття, – Гримайлів, 2003. – С. 333–338. 6. Оліяр Г.І. Фітораритети природного заповідника "Медобори" з філією "Кременецькі гори" в міжнародних червоних списках // Природно-заповідний фонд України – минуле, сьогодення, майбутнє. Матеріали міжнародної науковопрактичної конференції, присвяченої 20-річчю природного заповідника "Медобори" (смт. Гримайлів, 26–28 травня 2010 р.) – Тернопіль: Підручники і посібники, 2010. – С. 460–464. 7. Онищенко В.А. Рослинність карбонатних відслонень природного заповідника "Медобори" // Укр. фітоцен. зб. – Сер. A. – 2001. – 1 (17). – С. 86–104. 8. Онищенко В.А., Оліяр Г.І. ПЗ Медобори // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 254–276. 9. Смеречинская Т. А. Закономерности распространения лишайников по фитоценозам природного заповедника "Медоборы" // Заповідна справа в Україні. – 2005. – Т. 11, Вип. 1. – С. 9–15. 112 113 Hostra Skelia Ukrainian name: Гостра скеля. Transliteraion/Translaion variants: Gostra Skelya, Sharp Clif, Sharp Rock. Area: 8.0 ha. Altitude: 319–356 m. Latitude: 49°21'24" N (49.3565°). Longitude: 26°04'39" E (26.0774°). Administrative regions. Ternopil region: Husiatyn raion. Ownership: state. Biogeographic regions: coninental. H.I. Oliiar Hrakove N.O. Stetsiuk Ukrainian name: Гракове. Transliteraion/Translaion variants: Grakove. Area: 768 ha. Altitude: 80–85 m. Latitude: 49°34’32” N (49.5757°). Longitude: 32°54’57” E (32.9157°). Administrative regions. Poltava region: Semenivka raion. Ownership: state, municipal. Biogeographic regions: coninental. Habitats. Level 1. C – 7.8%; D – 23.4%; E – 68.1%; G – 0.7%. Habitats. Level 2. C1 Surface standing waters – 1.3%; C3 Littoral zone of inland surface waterbodies – 6.5%; D6 Inland saline and brackish marshes and reedbeds – 23.4%; E6 Salt steppes – 68.1%; G1 Broadleaved deciduous woodland – 0.7%. Land use: mowing/hay making – major, nature conservation and research – major. Protected areas: includes Hrakove state hydrological reserve (500 ha). Threats: abandonment/reducion of land management – low; agricultural intensiicaion/ expansion (general) – low. General description. Major vegetaion types are the halophyic wet and mesic grasslands dominated by Alopecurus arundinaceus, Beckmannia eruciformis, Carex distans, Juncus gerardii, Festuca regeliana, Puccinellia distans with presence of Carex secalina, Glaux mariima, Limonium alutaceum, Plantago salsa, Taraxacum bessarabicum, Triglochin mariima, Triglochin palustris. Large areas are covered by halophyic non-inundated Phragmites australis beds. There are marshes dominated by Bolboschoenus mariimus, Schoenoplectus tabernaemontani. On the most saline soils, there are communiies of Lepidium crassifolium with Salicornia herbacea, Halimione pedunculata, Halimione verrucifera. Brackish lakes are overgrown with Phragmites australis and Typha angusifolia. Botanical significance. One of the best sites with halophyic vegetaion in the coninental biogeographic region of Ukraine. Criterion A • Carex secalina Wahlenb.; A(ii); abundance: abundant; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E6.2 Coninental inland salt steppes; area: 500 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Байрак О.М., Проскурня М.І., Стецюк Н.О., Слюсар М.В., Томін Є.М., Гостудим О.М. Еталони природи Полтавщини. Розповідні про заповідні території Полтавщини. Науково-популярне видання. – Полтава: Верстка, 2003. – 212 с. Hranitno-Stepove Pobuzhia Futher habitat descripion. C1.5 Permanent inland saline and brackish lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D6.1 Inland saltmarshes; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E6.2 Continental inland salt steppes . V.A. Onyshchenko Ukrainian name: Гранітно-степове Побужжя. Transliteraion/Translaion variants: Granitno-Stepove Pobuzhzhya, Granite-Steppe Southern Buh Area. Area: 3815.0 ha. Altitude: 17–120 m. Latitude: 47°53’25” N (47.8903°). Longitude: 31°06’19” E (31.1053°). Administrative regions. Mykolaiv region: Arbuzynka raion, Domanivka raion, Pervomaisk raion, Voznesensk raion. Ownership: state, unknown. Biogeographic regions: steppic. Habitats. Level 1. C – 21.6%; D – 0.5%; E – 48.8%; F – 2.0%; G – 22.7%; H – 4.4% . Habitats. Level 2. C1 Surface standing waters – 5.0%; C2 Surface running waters – 16.5%; C3 Littoral zone of inland surface waterbodies – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.5%; E1 Dry grasslands – 48.6%; E2 Mesic grasslands – 0.1%; E3 Seasonally wet and wet grasslands – 0.1%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 22.7%; H2 Screes – 0.2; H3 Inland 114 115 cliffs, rock pavements and outcrops – 4.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.3 Permanent eutrophic lakes, ponds and pools; C2.2 Permanent non-idal, fast, turbulent watercourses; C2.3 Permanent non-idal, smooth-lowing watercourses; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.7 Thermophilous deciduous woodland; G1.C Highly ariicial broadleaved deciduous forestry plantaions; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – 15%; agriculture (arable) – minor; forestry – 15%; nature conservaion and research – 100%; water management – 7%. Protected areas: included in Buzkyi Hard naional nature park and Emerald Site “Bugzkyi Gard Naional Nature Park”. Threats: construcion/impact of dyke/dam/barrage – low; development (recreaion/ tourism) – low; forestry (aforestaion) – low. General description. The Southern Bug valley with high (10–60 m) steep slopes and clifs of granite and gneiss. Large areas are covered by the steppe vegetaion, natural Quercus robur termophilous woods, ariicial Quercus robur woods, steppic and loodplain scrub, loodplain decidous woods. Natural deciduous termophilous woods. Dominants: Quercus robur (major), Acer campestre, Fraxinus excelsior, Tilia cordata, Ulmus minor; Acer tataricum, Coinus coggygria, Crataegus fallacina, Euonymus europaeus, Eunymus verrucosus, Swida sanguinea. Typical species: Malus sylvestris, Pyrus communis; Chelidonium major, Galium aparine, Geum urbanum, Urica dioica. Floodplain woods. Dominants: Alnus gluinosa, Populus alba, Populus nigra, Salix alba, Salix fragilis. Shrubs. Dominant: Crataegus praearmata, Spiraea crenata, Prunus stepposa. Dry grasslands (steppes). Dominants: Sipa capillata, Sipa lessingiana, Festuca valesiaca, Botriochloa ischaemum, Koelerua cristata, Galatella villosa. Typical species: Artemisia marschalliana, Chamaecyisus austriacus, Galium verum, Medicago romanica, Poa angusifolia, Potenilla incana, Salvia nemorosa, Salvia nutans. Dominants in shrub steppes: Amygdalus nana, Caragana frutex. In steppes on shallow stony soils, typical species are Allium podolicum, Asperula rumelica, Genista inctoria, Pilosella oicinarum, Poa bulbosa, Seseli pallasii, Teucrium polium, Verbascum phoeniceum. Open silicious outcrops. Typical species: Achillea ochroleuca, Alyssum murale, Aurinia saxailis, Rumex fascilobus, Sedum acre, Sedum borissovae, Sempervivum ruthenicum, Thymus dimorphus; Ceratodon purpureus, Grimmia laevigata, Grimmia ovalis, Grimmia pulvinata, Polytrichum piliferum, Polytrichum juniperinum, Syntrichia ruralis, Tortula muralis. Shaded silicious outcrops. Dominants: Hypnum cupressiforme, Hedwigia ciliata, Homalothecium sericeum, Leucodon sciuroides. Typical species: Bryum capillare, Amblystegium serpens, Leskea polycarpa, Radula complanata. Litoral and mire vegetaion. Dominants: Agrosis stolonifera, Bolboschienus mariimus, Carex riparia, Glyceria maxima, Phalaroides arundinacea, Phragmites australis. Aquaic vegetaion. Dominants: Ceratophyllum demersum, Myriophyllum spicatum, Nuphar lutea, Potamogeton nodosus, Vallisneria spiralis. Botanical significance. Important for conservaion of endemic species of silicious outcrops (Dianthus hypanicus Andrz., Moehringia hypanica Grynj et Klokov, Cerasus klokovii Sobko, Sedum borissovae Balk., Silene hypanica Klokov, Silene sytnikii Krytzka, Novosad et Protopopova, Tulipa hypanica Klokov et Zoz, Onosma graniicola Klokov), dry grasslands, termophilous oak woods and steppic scrub. Criterion A • Cerasus klokovii Sobko; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Dianthus hypanicus Andrz.; A(i), A(ii), A(iii), abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Gymnospermium odessanum (DC.) Takht.; A(iv); abundance: unknown; trend: unknown; 116 117 species data quality: poor; trend data quality: poor. Moehringia hypanica Grynj et Klokov; A(i), A(ii); abundance: rare (one locality); trend: decreasing; species data quality: good; trend data quality: medium. • Onosma graniicola Klokov; A(iv); abundance: 400–500 individuals (one locality, 1.5–2.0 ha); trend: luctuaing; species data quality: good; trend data quality: medium. • Silene hypanica Klokov; A(iii); abundance: rare; trend: luctuaing; species data quality: good; trend data quality: medium. • Silene sytnikii Krytzka, Novosad et Protopopova; A(iii); abundance: occasional; trend: stable; species data quality: good; trend data quality: medium. • Tulipa hypanica Klokov et Zoz; A(iii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.11 Euro-siberian pioneer rock debris swards; area: 10 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 1500 ha; trend: stable; area data quality: medium; trend data quality: medium. • F3.247 Ponto-Sarmatic deciduous thickets; area: 75 ha; trend: stable; area data quality: medium; trend data quality: medium. • H3.1 Acid siliceous inland cliffs; area: 150 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Mikhailyuk T.I., Demchenko E.M., Kondratyuk S.Ya. Algae of granitе outcrops from the left bank of Pivdennyi Bug river (Ukraine) // Biologia. – Bratislava, 2003. – 58 (4). – P. 589–601. 2. Гревцова Г.Т. Кизильники гранітно-степового Побужжя // Збірник наукових праць Полтавського пед. ун-ту. – 2003. – Вип. 4 (31). – С. 54–61. 3. Гринь Ф.О., Клоков М.В. Новий вид мерингії з гранітів р. Південного Бугу // Бот. журн. АН УРСР. – 1950. – 7, № 4 – С. 55–60. 4. Деркач О.М. Доповнення до флори Правобережного степу України // Укр. бот. журн. – 1990. – 47, № 6. – С. 84–85. 5. Драбинюк Г.В. НПП Бузький Гард // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 49–60. 6. Коломієць Г.В., Таращук С.В. Бузькі брояки // Водно-болотні угіддя України. Довідник / під ред. Марушевського Г.Б., Жарук І.С. – К.: Чорноморська програма Ветландс Интернешнл. – 2006. – С. 188–193. 7. Михайлюк Т.И., Дариенко Т.М., Демченко Э.Н. Водоросли гранитных обнажений регионального ландшафтного парка “Гранитно-степное Побужье” (Николаевская обл., Украина) // Новости систематики низших растений. – 2003. – 37. – С. 53–71. 8. Новосад В.В., Крицкая Л.И., Протопопова В.В. Новий для науки ендемічний вид Гранітно-степового Побужжя смілка Ситника (Silene sytnikii Krytzka, Novosad et Protopopova), його таксономічні, еколого-ценотичні, хорологічні, генезисні та созологічні особливості // Укр. бот. журн. – 1996. – 53, № 5. – С. 578–585. 9. Партика Л.Я., Вірченко В.М., Нипорко С.О. 2006. До бріофлори регіонального ландшафтного парку “Гранітно-степове Побужжя” // Чорномор. ботан. журн. – 2006. – 2, № 1. – С. 116–122. 10. Собко В.Г. Ендемічні та реліктові елементи флори гранітних відслонень Придніпровської височини // Укр. бот. журн. – 1972. – 29, № 5. – C. 624–630. 11. Соломаха В.А., Драбинюк Г.В., Вініченко Т.С., Мойсієнко І.І., Деркач О.М. Адаптивні особливості південнобузьких ендемів Dianthus hypanicus Andrz. та Moehringia hypanica Grynj et Klok. // Укр. фітоцен. зб. – Сер. С. – 2006. – Вип. 24. – С. 70–86. 12. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 13. Щербакова О.Ф. Особливості популяційної структури чистецю вузьколистого Stachys angustifolia M. Bieb в Гранітно-Степовому Побужжі та проблеми його охорони // Актуальні проблеми ботаніки та екології. Збірн. наук. праць. – 2005. – Вип. 1. – С. 96–104. 14. Щербакова О.Ф., Новосад В.В., Крицька Л.І. Раритетний флорофонд КодимоЄланецького Побужжя (ЧКУ, 2009): популяційні та флоросозологічні аспекти. Рослинний світ у Червоній книзі України: впровадження Глобальної стратегії збереження рослин. Мат-ли міжнар. конф. (11–15 жовтня 2010 р., м.Київ). – Київ: Альтерпрес, 2010. – С. 210–214. 118 119 • Ihrovets – Tavpishyrka V.A. Onyshchenko, R.Ya. Kish Ukrainian name: Ігровець – Тавпіширка. Area: 6538.0 ha. Altitude: 1062–1836 m. Latitude: 48°32’36” N (48.5433°). Longitude: 24°07’15” E (24.1207°). Administrative regions. Ivano-Frankivsk region: Bohorodchany, Nadvirna raion, Rozhniaiv; Zakarpatska region: Tiachiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. E – 0.6%; F – 16.8%; G – 78.6%; H – 4.0%. Habitats. Level 2. F2 Arctic, alpine and subalpine scrub – 16.8%; G1 Broadleaved deciduous woodland – 0.4%; G3 Coniferous woodland – 77.7%; G4 Mixed deciduous and coniferous woodland – 0.5%; H2 Screes – 3.8%; H3 Inland cliffs, rock pavements and outcrops – 0.2%. Futher habitat description. F2.4 Conifer scrub close to the tree limit; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H3.1 Acid silicious inland clifs. Land use: forestry – minor; nature conservation and research – minor. Protected areas: overlaps with Tavpyshyrkivskyi state botanical reserve (about 390 ha), includes state botanical reserve “Gorgany i Tavpishyrka” (248 ha), includes Syvulia regional nature preserve (17 ha), includes Tavpishyrka regional nature preserve (33 ha), overlaps with regional nature preserve “Urochyshche Salatruk” (about 100 ha), overlaps (1476 ha) with Emerald Site “Dolynsko-Rozhniatynskyi”. Threats: climate change/sea level rise – low, forestry (intensiied forest management) – low. General description. Forests dominated by Picea abies, Pinus mugo shrub, coarse sandstone. Dominants of the lower layers of the spruce woods areLower layers are dominated by Vaccinium myrillus, Homogyne alpina, Oxalis acetosella, Calamagrosis arundinacea. Small areas are occupied by Pinus cembra woods. Botanical significance. Important area for communiies of Pinus mugo, Carpathian Pinus Irpinskyi Lis Ukrainian name: Ірпінський ліс. Transliteraion/Translaion variants: Irpin’ Forest. Area: 307.0 ha Altitude: 112-165 m. Latitude: 50°30’42” N (50.5115°). Longitude: 30°16’37” E (30.2769°). Administraive regions. Kyiv city: Sviatoshyn raion. Ownership: state. Biogeographic regions: coninental. cembra forests and subspecies Larix decidua ssp. polonica. Criterion C • F2.46 (*4070) Carpathian Pinus mugo scrub; area: 1100 ha; trend: stable; area data quality: good; trend data quality: poor. • G3.25 Carpathian Larix and Pinus cembra forests; area: 15 ha; trend: decreasing; area data quality: medium; trend data quality: medium. 120 V.A. Onyshchenko, O.I. Pryadko Habitats. Level 1. G – 98.0%; H – 2.0% Habitats. Level 2. G1 Broadleaved deciduous woodland – 42.0%; G3 Coniferous woodland – 2.0%; G4 Mixed deciduous and coniferous woodland – 50.0%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 4.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 2.0%. Futher habitat description. G1.7 Thermophilous deciduous woodland; G3.4 Pinus sylvestris woodland south of the taiga, G4.C Mixed Pinus sylvestris – thermophilous Quercus woodland, H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – major. Protected areas: included in Holosiivskyi naional nature park, included in Emerald Site 121 “Holosiivskyi Naional Nature Park”. Threats: unsustainable plant exploitaion – low. General description. A part of the terrace of the Irpin river over the loodplain. Quercus robur and mixed Quercus robur - Pinus sylvestris forest with the herb layer dominated by Carex michelii, Clemais recta, Convallaria majalis. Constant species: Agrosis capillaris, Convallaria majalis, Campanula bononiensis, Cruciata glabra, Euphorbia cyparissias, Fallopia dumetorum, Festuca rubra, Fragaria vesca, Frangula alnus, Galeopsis bifida, Galium mollugo, Geranium roberianum, Geranium sanguineum, Geum urbanum, Hylotelephium polonicum, Hypericum perforatum, Impaiens parvilora, Malus sylvestris, Melampyrum nemorosum, Moehringia trinervia, Peucedanum oreoselinum, Pinus sylvestris, Polygonatum odoratum, Populus tremula, Potenilla alba, Pteridium aquilinum, Pyrus communis, Quercus robur, Stachys officinalis, Solidago virgaurea, Sorbus aucuparia, Torilis japonica. Botanical significance. One of the largest populaions of Iris hungarica in Ukraine. Criterion A • Iris hungarica Waldst. & Kit.; A(ii); abundance: frequent (~1000 clones); trend: stable; species data quality: medium; trend data quality: poor. Conservation proposals: include in the zone of strict protecion of the Holosiivskyi naional nature park. Literature 1. Онищенко В.А., Прядко О.І., Арап Р.Я., Дацюк В.В. Світлі дубові ліси СвятошинськоБіличанського відділення НПП “Голосіївський” // Природоохороні території в минулому, сучасному й майбутньому світі (до 130-річчя створення “Пам’ятки Пеняцької” – першої природоохоронної території у Європі): Мат-ли Другої міжнародної конференції (Львів – Броди – Пеняки, 26–27 жовтня 2016 року). – Львів: Ліга-Прес, 2016. – С. 189–192. dominated by Bothriochloa ischaemum, Carex humilis, Elytrigia intermedia, Festuca valesiaca, Koeleria cristata, Poa angustifolia, Stipa capillata. Other frequent species are Achillea submillefolium, Agrimonia eupatoria, Asperula cynanchica, Astragalus austriacus, A. onobrychis, Chamaecytisus podolicus, Filipendula vulgaris, Fragaria viridis, Galium verum, Gypsophila thyraica, Inula ensifolia, Knautia arvensis, Onobrychis arenaria, Pimpinella saxifraga, Potentilla arenaria, Poterium sanguisorba, Ranunculus polyanthemos, Salvia pratensis, S. verticillata, Securigera varia, Teucrium chamaedrys, T. pannonicum, Thalictrum minus, Thymus marschallianus, Trifolium montanum, Viola hirta. Kadubivska Sinka I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Кадубівська стінка. Transliteraion/Translaion variants: Kadubivska Wall, Kadubivska Clif. Area: 27.0 ha. Altitude: 226-270 m. Latitude: 48°34’02” N (48.5672°). Longitude: 25°45’55” E (25.7653°). Administraive regions. Chernivtsi region: Zastavna raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 99.0%; F – 0.7%; H – 0.3% Habitats. Level 2. E1 Dry grasslands – 99.0%; F3 Temperate and mediterranean-montane scrubs – 0.7%; H3 Inland cliffs, rock pavements and outcrops – 0.3%. Futherhabitat description: E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; H3.2 Basic and ultra-basic inland clifs. Landuse: agriculture (animals) – major; nature conservaion and research – major. Protected areas: includes Kadubivska Sinka state landscape reserve (22.8 ha). Threats: agricultural intensiicaion/expansion (grazing) – low. General description. Slopes with grasslands and gypsum outcrops. Grasslands are 122 Botanical significance. One of the largest populaions of Chamaecytisus podolicus, locus classucus of this species. The area is important also for Gypsophila thyraica and Iris hungarica. Criterion A • Chamaecytisus podolicus (Błocki) Klásk. A(iv); abundance: frequent; trend: unknown; 123 species data quality: good; trend data quality: poor. Gypsophila thyraica A.Krasnova A(iiі); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. • Iris hungarica Waldst. & Kit.; A(ii); abundance: rare; trend: unknown; species data quality: good; trend data quality: poor. Literature 1. Коротченко І.А., Токарюк А.І. Флора та рослинність степів ландшафтного заказника “Кадубівська стінка” (Чернівецька область) // Наук. вісник Чернівецкого унту: Зб. наук. праць. – Чернівці: Рута, 2004. – Вип. 194. – С. 117–127. 2. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. 3. Чорней І.І., Скільський І.В., Коржик В.П., Буджак В.В. Заповідні об’єкти Буковини загальнодержавного значення як основа регіональної екологічної мережі // Заповідна справа в Україні. – 2001. – Т. 7, вип. 2. – С. 73–98. • major dominants are Festuca valesiaca and Sipa capillata. Typical species are Euphorbia seguierana, Herniaria kotovii, Artemisia austriaca. On stony soils, there dominates Sipa graiicola and Thymus graniicus. On rocks, there are Erodium beketowii, Asperula graniicola, Rumex fascilobus, Jurinea graniicola, Hedysarum grandilorum, Scophularia graniica. Botanical significance. Important area for conservaion of the steppe vegetaion. Kalmiuskyi Step V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Кальміуський степ Transliteraion/Translaion variants: Kal’mius Steppe. Area: 2994.0 ha. Altitude: 40–130 m. Latitude: 47°30’39” N (47.5107°). Longitude: 37°55’33” E (37.9257°) Administrative regions. Donetsk region: Boikivske (Telmanove) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.8%; E – 96.0%; F – 0.5%; G – 1.7%; H – 1.0%. Habitats. Level 2. C2 Surface running waters – 0.6%; C3 Littoral zone of inland surface waterbodies – 0.1%; E1 Dry grasslands – 94.0%; E2 Mesic grasslands – 2.0%; F3 Temperate and mediterranean-montane scrub – 0.5%; G1 Broadleaved deciduous woodland – 0.1%; G3 Coniferous woodland – 1.6%; H2 Screes – 0.2%; H3 Inland cliffs, rock pavements and outcrops – 0.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; G3.F Highly artificial coniferous plantations; H2.5 Acid siliceous screes of warm exposures, H3.1 Acid silicious inland clifs. Land use: agriculture (animals) – major; nature conservaion and research – major. Protected areas: overlaps (579.6 ha) with Ukrainskyi Stepovyi nature reserve (includes division “Kalmiuske” of the reserve), overlaps (579.6 ha) with Emerald Site “Ukrainskyi Stepovyi Nature Reserve”. Threats: agricultural intensification/expansion (arable) – low, agricultural intensiicaion/ expansion (grazing) – low, extracion (minerals/quarries) – low. General description. The valleys of the Kalmius river and its tributary with the steppe vegetaion and granite outcrops. The steppe vegetaion occupies the largest area. Its 124 Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 2500 ha; trend: stable; area data quality: good; trend data quality: good Literature 1. Коломійчук В.П., Остапко В.М., Яровий С.С. ПЗ Український степовий // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 336–378. 2. Ткаченко В.С., Генов А.П. Флороценотична характеристика запропонованого Кальміуського державного заказника // Укр. ботан. журн. – 1986. – 43, № 5. – С. 92–96. 125 Kamiani Mohyly V.A. Onyshchenko, V.P. Kolomiychuk Ukrainian name: Кам’яні могили. Transliteraion/Translaion variants: Kam’yani Mogyly, Rocky Hills. Area: 438.0 ha. Altitude: 123–206 m. Latitude: 47°18’23” N (47.3065°). Longitude: 37°04’48” E (37.0800°). Administrative regions. Donetsk region: Volodarske raion. Zaporizhia region: Rozivka raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.4%; D – 0.4%; E – 83.7%; F – 5.0%; G – 0.5%; H – 10.0%. Habitats. Level 2. C3 Littoral zone of inland surface waterbodies – 0.4%; D5 Sedge and reedbeds, normally without free-standing water – 0.4%; E1 Dry grasslands – 81.1%; E2 Mesic grasslands – 2.6%; F3 Temperate and mediterranean-montane scrub – 5.0%; G1 Broadleaved deciduous woodland – 0.5%; H3 Inland cliffs, rock pavements and outcrops – 2.0%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; F3.1 Temperate thickets and scrub; F3.2 Submediterranean 126 deciduous thickets and brushes; H2.5 Acid siliceous screes of warm exposures, H3.1 Acid silicious inland clifs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: agriculture (animals) – minor; nature conservaion and research – major. Protected areas: includes division “Kamiani Mohyly “ of Ukrainskyi Stepovyi nature reserve (389.2 ha), overlaps (389.2 ha) with Emerald Site “Ukrainskyi Stepovyi Nature Reserve”. Threats: –. General description. Protected area with the steppe vegetaion and hills with outcrops of granite. Main dominants are Poa angusifolia and Elytrigia trichophora. Species of high constancy are Achillea setacea, Artemisia absinthium, Euphorbia stepposa, Falcaria vulgaris, Festuca valesiaca, Galatella villosa, Medicago falcata, Phlomoides tuberosa (Phlomis tuberosa), Salvia nemorosa, Sipa capillata, Teucrium polium, Thalictrum minus, Verbascum austriacum. On more stony solils, there are plant communiies dominates by Festuca valesiaca, Sipa capillata, Sipa lessingiana with presence of Achillea setacea, Cota inctoria (Anthemis inctoria), Artemisia austriaca, Bromopsis riparia, Centaurea trinervia, Filipendula vulgaris, Galatella villosa, Hypericum perforatum, Marrubium praecox, Odonites luteus, Potenilla argentea, Salvia nutans, Scabiosa ochroleuca, Securigera varia, Stachys recta, Thymus dimorphus, Thymus marschallianus. Prevailng dominant of the shrub vegetaion is Prunus stepposa. On granite rocks, there are Allium decipiens, Allium lavescens, Asplenium septentrionale, Asplenium trichomanis, Aurinia saxailis, Centaurea pseodoleucolepis, Festuca valesiaca, Oites hellmannii, Rosa subpygmaea, Spiraea hypericifolia. Botanical significance. Two species have all their natural range inside this area: Achillea glaberrima, Centaurea pseudoleucolepis. Important area for conservaion of steppe thickets and siliceus outcrops. Criterion A • Achillea glaberrima Klokov; A(ii); abundance: frequent (8 000 000 individuals); trend: stable; species data quality: good; trend data quality: good. • Astragalus tanaiicus K. Koch.; A(i), A(ii); abundance: rare; trend: luctuaing; species data quality: medium; trend data quality: poor. • Centaurea pseudoleucolepis Kleopow.; A(i), A(ii); abundance: frequent (150 000 individuals); trend: decreasing; species data quality: good; trend data quality: good. Criterion C • F3.247 Ponto-Sarmatic deciduous thickets; area: 20 ha; trend: increasing; area data quality: good; trend data quality: good. • H3.1 Acid siliceous inland cliffs; area: 1 ha; trend: stable; area data quality: medium; trend data quality: good. Note: On the site, there prevail horizontal granite outcrops (about 30 ha) that are not meet the habitat type H3.1 including only verical outcrops. Literature 1. Білик Г.І., Панова Л.С. Поновлення степової рослинності в заповіднику Кам’яні Могили після припинення випасання // Укр. ботан. журн. – 1970. – 27, № 6. – С. 711–715. 2. Бойко М.Ф. Участь мохоподібних у формуванні фітоценозів заповідника “Кам’яні Могили” // Укр. ботан. журн. – 1979. – 36, № 5. – С. 478–483. 3. Коломійчук В.П., Остапко В.М., Яровий С.С. ПЗ Український степовий // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 336–378. 4. Лисенко Г.М. Моніторинг фітосистем заповідного степу “Кам’яні Могили” // Чорноморський ботанічний журнал. – 2008. – 65, № 1 – С. 89–97. 5. Осычнюк В.В., Генов А.П., Генова Л.Ф. Флора Украинского степного заповедника 127 (аннотированный список сосудистых растений). – М., 1988. – 44 с. 6. Ткаченко В.С. Резерватні сукцесії та охоронний режим степової рослинності в заповіднику “Кам’яні Могили” // Укр. ботан. журн. – 1992. – 49, № 6. – С. 18–22. 7. Ткаченко В.С., Генов А.П., Сіренко В.О. Саморозвиток фітосистем заповідного степу “Кам’яні Могили” (Донецька область) // Український ботанічний журнал. – 2003. – 60, № 3. – С. 248–255. 8. Ткаченко В.С., Дідух Я.П., Генов А.П. та ін. Український природний степовий заповідник. Рослинний світ. – К.: Фітосоціоцентр, 1998. – 280 с. Polygonum hydropiper, Rubus caesius, Symphytum oicinale. Main dominants of shrub communiies are Amorpha fruicosa and Salix acuifolia. Psammophyic communiies dominated by Koeleria glauca s.l., Festuca beckeri, Secale sylvestre, Calamagrosis epigeios, Carex colchica, Sedum sexangulare and unmanaged mesic and wet grasslands dominated by Alopecurus pratensis, Arrhenatherum elaius, Carex praecox, Elytrigia repens, Festuca pratensis, Graiola oicinalis, Lycopus exaltatus, Lysimachia vulgaris, Lythrum salicaria, Lythrum virgatum, Poa palustris occupy about 200 ha. Kanivski Ostrovy V.A. Onyshchenko Ukrainian name: Канівські острови. Transliteraion/Translaion variants: Kaniv Islands. Area: 1136 ha. Altitude: 81–89 m. Latitude: 49°42’16” N (49.7045°). Longitude: 31°55’14” E (31.5873°). Administrative regions. Cherkasy region: Kaniv raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. C – 40%; D – 2%; E – 16%; F – 17%; G – 25%. Habitats. Level 2. C1 Surface standing waters – 10%; C2 Surface running waters – 28%; C3 Littoral zone of inland surface waterbodies – 2%; D5 Sedge and reedbeds, normally without free-standing water – 2%; E1 Dry grasslands – 5%; E3 Seasonally wet and wet grasslands – 8%; E5 Woodland fringes and clearings and tall forb stands – 3%; F9 Riverine and fen scrubs – 17%; G1 Broadleaved deciduous woodland – 25%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; C3.5 Periodically inundated shores with pioneer and ephemeral vegetation; C3.6 Unvegetated or sparsely vegetated shores with soft or mobile sediments; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.3 Mediterranean riparian woodland. Land use: conservation and research – 44%. Protected areas: overlaps (686 ha) with Kanivskyi nature reserve, overlaps (686 ha) with Emerald Site “Kanivskyi Nature Reserve”. Threats: abandonment/reduction of land management – low. General description. Several loodplain islands of variable coniguraion in the valley of the Dnipro. A big area is occupied by riverine woods and shrubs. Tree layer of the woods is dominated by Populus alba, Populus nigra, Salix alba. Species of high constancy: Acer negundo, Aristolochia clemaiis, Galium verum, Myosois palustris, Poa nemoralis, 128 Botanical significance. The area is noted for conservaion of comlexes of a big river (forests, shrubs, litoral and aquaic vegetaion). Criterion C • C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; area: 1 ha; trend: luctuaing; area data quality: poor; trend data quality: medium 129 • C3.51 Euro-Siberian dwarf annual amphibious swards; area: 3 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E5.4 Moist or wet tall-herb and fern fringes and meadows; area: 30 ha; trend: unknown; area data quality: poor; trend data quality: poor. • F9.1 Riverine scrub; area: 180 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.11 Riverine Salix woodland; area: 80 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.3 Mediterranean riparian woodland; area: 200 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Шевчик В.Л. ПЗ Канівський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 151–169. 2. Шевчик В.Л., Соломаха В.А. Синтаксономія рослинності островів Круглик та Шелестів Канівського природного заповідника // Укр. фітоцен. зб., 1997. – Сер. А, Вип. 1. – С. 12–27. 3. Шевчик В.Л., Соломаха В.А., Войтюк Ю.О. Синтаксономія рослинності та список флори Канівського природного заповідника // Укр. фітоцен. зб, 1996. – Сер B., Вип. 1. – С. 1–119. Brachypodium sylvaicum, Viola mirabilis, Lathyrus vernus, Hedera helix, Hepaica nobilis. Botanical significance. One of the best populaions of Friillaria montana in Ukraine. Kaplivka I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Каплівка. Area: 32.8 ha. Altitude: 192-232 m. Latitude: 48°25’33” N (48.4258°). Longitude: 26°33’16” E (26.5545°). Administraive regions: Chernivtsi region: Khotyn raion. Ownership: state. Biogeographiczones: coninental. Habitats. Level 1. G1 – 100.0%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 100.0 %; Futher habitat description: G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Landuse: forestry – major. Protected areas: –. Threats: forestry (intensiied forest management) – medium. General description. Broadleaved forest with dominance of Quercus robur and signiicant admixture of Tilia cordata, Carpinus betulus, Fraxinus excelsior, Acer campeste, Acer pseudoplatanus, Acer platanoides, Cerasus avium. The shrub layer consists of Acer tataricum, Swida sanguinea (Cornus sanguinea), Corylusa avellana, Sambucus nigra, Euonymus europaeus, Euonymus verrucosus, Viburnum lantana. Typical species of the herb layer are: Isopyrum thalictroides, Ficaria verna, Corydalis cava, Corydalis solida, Arum besserianum, Polygonatum hirtum, Pulmonaria obscura, Aegopodium podagraria, Asarum europaeum, Criterion A • Fritillaria montana Hoppe; А (ii); abundance: rare; trend: stable; species dataquality: good; trend data quality: poor. Conservaion proposals. Create a state botanical reserve and an Emerald Site. Literature 1. Каземірська М.А., Чорней І.І. Вікова та просторова структури популяцій Fritillaria montana Hoppe у Прут-Дністровському межиріччі // Біологічні системи. – 2010. – Т. 2., Вип. 2. – С. 62-66. 2. Каземірська М.А., Токарюк А.І., Чорней І.І. Насіннєва продуктивність Fritillaria montana Hoppe (Liliaceae) в популяціях на північно-східній межі ареалу (середнє ПрутДністров’я) // Заповідна справа в Україні. – 2010. – Т. 16, вип. 2.. – С. 9-14. 3. Каземірська М.А., Чорней І.І. Fritillaria montanaHoppe (Liliaceae): географічна характеристика, поширення в Україні // Науковий вісник Чернівецького університету. Біологія (Біологічні системи). – 2010. – Т. 2, Вип. 3. – С. 63-68. 4. Каземірська М.А., Чорней І.І. Стан популяцій Friillaria montana Hoppe (Liliaceae) на крайній північно-східній межі ареалу // Ботаніка та мікологія: проблеми і перспективи на 2011-2020 роки (Матеріали Всеукраїнської наукової конференції, Київ, 6-8 квітня 2011 року) / Під. ред. І.О. Дудки та С.Я. Кондратюка. – К.: Інститут ботанікиім. М.Г. Холодного, 2011. – С. 65-67. 5. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. 130 131 Karadah V.A. Onyshchenko Ukrainian name: Карадаг. Transliteraion/Translaion variants: Karadag, Kara Dag, Kara Dağ. Area: 3001.0 ha. Altitude: 0–577 m. Latitude: 44°55’56” N (44.9323°). Longitude: 35°13’25” E (35.2236°). Administrative regions. Autonomous Republic of Crimea: Feodosia city; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 24.0%; B – 0.2%; E – 17.5%; F – 3.3%; G – 47.0%; H – 8.0%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.1%; A2 Littoral sediment – 0.1%; A3 Infralittoral rock and other hard substrata – 15.5%; A5 Sublittoral sediment – 8.3%; 132 B2 Coastal shingle – 0.1%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.1%; E1 Dry grasslands – 17.5%; F3 Temperate and mediterranean-montane scrub – 1.3%; F7 Spiny Mediterranean heaths – 2.0%; F9 Riverine and fen scrubs – 0.0%; G1 Broadleaved deciduous woodland – 36.4%; G3 Coniferous woodland – 10.6%; H2 Screes – 1.0%; H3 Inland clifs, rock pavements and outcrops – 6.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.1 Litoral coarse sediment; A2.5 Coastal saltmarshes and saline reedbeds; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.5 Sublitoral macrophyte-dominated sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E1.3 Mediterranean xeric grassland; F3.2 Submediterranean deciduous thickets and brushes; F7.4 Hedgehog-heaths; F9.3 Southern riparian galleries and thickets; G1.7 Thermophilous deciduous woodland; G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; G3.9 Coniferous woodland dominated by Cupressaceae or Taxaceae; G3.F Highly ariicial coniferous forestry plantations; G5.61 Deciduous shrub woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservaion and research – 95%; tourism/recreaion – minor. Protected areas: overlaps (2860 ha) with Karadazkyi nature reserve, overlaps (2860 ha) with Emerald Site “Karadazkyi Nature Reserve”. Threats: development (recreaion/tourism) – low, eutrophicaion – low. General description. IPA is located in the eastern part of the Crimean mounains and includes 809 ha of the Black Sea. A part of the area are typical of Crimea. Mountains of this territory are composed of limestone. Closer to the sea, there prevail volcanic rocks (tufs, liparites). The largest area (about 600 ha) is occupied by mesic Quercus pubescens forests with the shrub layer dominated by Cornus mas. Aegonychon purpureo-caeruleum prevails in the herb layer. Constant species are Acer campestre, Asparagus vericillatus, Carex hallerana, Dictamnus gymnostylis, Laser trilobum, Mercurialis perennis, Paeonia daurica, Physospermum cornubiense, Polygonatum hirtum. Besides there are about 200 ha of dry open Quercus pubescens woods with Paliurus spina-chrisi, Juniperus oxycedrus, Pyrus eleagnifolia, Jasminum fruicans, Coinus coggygria, Rosa canina s.l., Festuca rupicola, Festuca callieri, Elytrigia nodosa. At higer alitudes, there are Quercus petraea woods with dominance or co-dominance of Carpinus betulus, Physospermum cornubiense, Mercurialis perennis, Galanthus plicatus, Corydalis marschalliana and Fraxinus excelsior woods with dominance of Physospermum cornubiense and Ranunculus constantinopolitanus in the herb layer. Open woods of Juniperus excelsa occupy about 37 ha. Steppe vegetaion covers about 400 ha. Typical dominants of the steppe vegetaion are Festuca valesiaca, Festuca callieri, Sipa ponica; species of high constancy: Achillea nobilis, Aegilops triuncialis, Botriochloa ischaemum, Centaurea difusa, Filipendula vulgaris, Galatella villosa, Helianthemum salicifolium, Inula oculus-chrisi, Jurinea sordida, Koeleria cristata, Thesium arvense, Teucrium polium, Veronica capsellicarpa, Velezia rigida. Steppes dominated by Bromopsis cappadocica or Sipa brauneri occur on stony soils. Steppes dominated by Elytrigia nodosa, Agropyron ponicum, A. pecinatum have high constacies of Alyssum 133 hirsutum, Alyssum umbellatum, Bromus squarrosus, Crupina vulgaris, Eryngium campestre, Jurinea stoechadifolia, Poa sterilis. Ephemeral grasslands dominated by Aegilops triuncialis, Anisantha sterilis, Anisantha tectorum occupy about 40 ha. In summer Cynodon dactylon and Elytrigia repens dominate in these places. Major dominants of marine vegetaion on sublitoral rock, boulders and pebble are Cladophora dalmaica, Cladostephus vericillatus, Corallina mediterranea, Cystoseira crinita, Cystosera barbata, Phyllophora nervosa. At oligotrophic sites at depth 1–5 m, there occur communiies co-dominated by Dilophus fasciola f. repens, Polysiphonia opaca, Ceramium ciliatum, Enteromorpha compressa. Polysiphonia elongata and Zanardinia prototypus dominate on sand at depth more than 15 m. Nemalion helminthoides and Laurencia papillosa dominates on litoral rocks, Enteromorpha linza and Ulva rigida – on stones at the water’s edge at eutrophic sites. Decreasing trend in biomass of algae and in area of oligotrophic communiies exists because of eutrophicaion of the sea. Botanical significance. This area is the richest in narrow endemic species part of Ukraine. Flora of Karadah includes two narrow endemic species: Cerasium stevenii, Crataegus pojarkovae. Important area for conservaion of deciduous woods, Juniperus excelsa woodlands, dry grasslands, tomillares and marine vegetaion. Criterion A • Astracantha arnacantha (M.Bieb.) Podlech; A(iv); abundance: frequent, 5000 individuals; trend: stable; species data quality: good; trend data quality: poor. • Centaurea sarandinakiae Illar.; A(iv); abundance: occasional, >500 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Cephalaria demetrii Bobrov; A(iii); abundance: rare, 150 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Crambe aspera M. Bieb.; A(iv); abundance: rare, 100 individuals in 2 localities; trend: unknown; species data quality: good; trend data quality: poor. • Crambe koktebelica (Junge) N.Busch; A(ii); abundance: >100 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Crambe pinnaiida W.T.Aiton.; A(iv); abundance: rare; trend: unknown; species data quality: good; trend data quality: poor. • Crambe steveniana Rupr.; A(iv); abundance: rare; trend: unknown; species data quality: good; trend data quality: poor. • Crataegus pojarkovae Kossych; A(iii); abundance: rare, 100 individuals; trend: stable; species data quality: good; trend data quality: poor. • Eremurus tauricus Steven; A(iv); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. • Himantoglossum caprinum (Bieb.) C.Koch.; A(ii), A(iv); abundance: frequent, >8000 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Onobrychis pallasii (Willd.) M.Bieb.; A(iii); abundance: rare, 150 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Onosma polyphylla Ledeb.; A(ii), A(iv); abundance: occasional, 3000 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Ophrys oestrifera Bieb.; A(ii); abundance: rare, 120 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Orchis punctulata Steven ex Lindl.; A(ii); abundance: rare, 40 individuals; trend: unknown; species data quality: good; trend data quality: poor. • Rhus coriaria L.; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: medium. • Sipa poëica Klokov; A(iv); abundance: occasional; trend: unknown; species data quality: poor; trend data quality: poor. Sipa syreistschikowii P.Smirn.; A(ii), A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Tilia dasystyla Stev.; A(iv); abundance: rare, 70 generaive individuals; trend: unknown; species data quality: good; trend data quality: poor. Criterion B • G1 deciduous broadleaved woodland; area 1090 ha; % of indicator species: 30.0%; No of indicator species: 20; trend: increasing; species data quality: good; area data quality: good; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 300 ha; trend: stable; area data quality: medium; trend data quality: medium . • F7 Spiny Mediterranean heaths; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. • G3.9 Coniferous woodland dominated by Cupressaceae or Taxaceae; area: 37 ha; trend: stable; area data quality: medium; trend data quality: medium. • H3.2 Basic and ultra-basic inland cliffs; area: 200 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Безнис Н.Г., Копачевская Е.Г. Лишайники Карадагского государственного заповедника // V съезд Украин. ботан. о-ва (Ялта, апрель 1982 г.). – Киев: Наукова думка. – 1982. – С. 333. 2. Вассер С.П., Бухтіярова Л.Н. Прісноводні діатомові водорості (Вaccilariophyta) Ялтинського та Карадазького заповідників // Укр. ботан. журн. – 1990. – 47. – № 6. – С. 28–30. 3. Виноградова О.М. Синьозелені водорості грунтів Карадазького державного заповідника // Укр. ботан. журн. – 1989. – 46, № 1. – С. 40–45. 4. Виноградова О.Н. Сyanophyta водоемов Карадагского государственного заповедника (Крым, Украина) // Альгология. – 1995 . – 5. – № 3. – С. 276–286. 5. Войцехович А.А. Фотобионты и водоросли-эпифиты литофильных лишайников Берегового хребта Карадагского природного заповедника (Крым, Украина) // Актуальні проблеми ботаніки та екології. Вип. 2. – Київ: Фітосоціоцентр. – 2008. – С. 46–51. 6. Войцехович А.О., Димитрова Л.В. Нові та цікаві знахідки представників родів Printzina R.H.Thomps. et Wujek. і Trentepohlia C.F.P. Maretius (Trentepohliaceae, Chlopophyta) // Укр. ботан. журн. – 2011. – 68, № 5. – С. 739–752. 7. Гелюта В.П., Андріанова Т.В. Фітопатогенні філофільні та гербофільні гриби Карадагського державного заповідника // Укр. ботан. журн. – 1984. – 41. – № 4. – С. 33–37. 8. Гелюта В.П. Видовий склад борошнисто-росяних грибів (Еrysiphaceae) Карадагського державного заповідника // Укр. ботан. журн. – 1985. – 42. – № 5. – С. 36–39. 9. Гелюта В.П. Розподіл борошнисто-росяних грибів (Еrysiphaceae) за рослинними угрупованнями Карадазького державного заповідника // Укр. ботан. журн. – 1986. – 43. – № 6. – С. 12–15. 10. Генералова В.Н. Водоросли Черного моря района Карадагской биологической станции // Труды Карадагской биологической станции. – 1950. – Вып. 10. – С. 106–147. 11. Дарієнко Т.М. Почвенные водоросли заповедников Горного Крыма (Украина) // Альгология. – 2000. – 10, №1. – С. 54–62. 134 135 • 12. Дидух Я.П., Вакаренко Л.П., Шеляг-Сосонко Ю.Р. Геоботаническая карта Карадага (Крым) как основа для изучения антропогенных сукцессий растительности // Геоботаническое картографирование. – Л.: Наука, Ленинградское отделение. – 1981. – С. 25–33. 13. Дидух Я.П., Шеляг-Сосонко Ю.Р. Карадагский государственный заповедник. Растительный мир. – Киев: Наук. думка, 1982. – 152 с. 14. Дикий Є.О. Сукцесії донної рослинності шельфу південно-східного Криму. Автореферат дисс... канд. біол. наук. – Київ, 2007. – 23 с. 15. Згуровская Л.Н. Сравнение таксономического состава диатомовых водорослей в планктоне и в донных осадках у берегов Карадага // Океанология. – 1979. – 9. – Вып. 6. – С. 1087–1093. 16. Ісіков В.П. Ксилотрофні мiкроміцети Криму // Укр. ботан. журн. – 2003. – 60, № 4. – С. 447–463. 17. Калугина-Гутник А.А. Донная растительность района Карадага Черного моря и ее изменения за последние 20 лет // Биология моря. – Киев. – 1976. – Вып. 36. – С. 3–17. 18. Калугина-Гутник А.А. Изменение донной растительности района Карадага за период 1970–1980 гг. // Многолетняя динамика структуры прибрежных экосистем Черного моря. – Краснодар: Кубанский госуниверситет. – 1984. – С. 85–96. 19. Карадаг. Гидробиологические исследования (Сборник научных трудов, посвящённый 90-летию Карадагской научной станции им. Т.И. Вяземского и 25-летию Карадагского природного заповедника НАН Украины). Книга 2-я. / Под ред. А.Л. Морозовой, В.Ф. Гнюбкина. – Симферополь: СОНАТ, 2004. – 500 с. 20. Карадаг. История, биология, археология (Сборник научных трудов, посвящённый 85-летию Карадагской биологической станции им. Т.И. Вяземского) / Под ред. А.Л. Морозовой, В.Ф. Гнюбкина. – Симферополь: СОНАТ, 2001. – 304 с. 21. Карадаг – 2009: Сборник научных трудов, посвящённый 95-летию Карадагской научной станции и 30-летию Карадагского природного заповедника Национальной академии наук Украины / Ред. А.В. Гаевская, А.Л. Морозова. – Севастополь: ЭКОСИГидрофизика, 2009. – 575 с 22. Клюкин А.А., Костенко Н.С. Воздействие экстремальных штормов на рельеф и прибрежные сообщества эпибентоса Крыма // Гидробиологические исследования в заповедниках. – Вып. 8. – М. – 1996. – С. 140–150. 23. Костенко Н.С. Картирование фитобентоса акватории Карадагского государственного заповедника АН УССР (Черное море) // Ботан. журн. – 1988. – 73, №11. – С. 1590–1596. 24. Костенко Н.С. Антропогенные изменения донной растительности Карадагского заповедника // Научные доклады высшей школы. Биологические науки. – М.: Высшая школа. – 1990. – № 9 (321). – С. 101–110. 25. Костенко Н.С. 100-летие гидробиологических исследований на Карадаге: итоги и перспективы // Заповедники Крыма. Биоразнообразие и охрана природы в Азово-Черноморском регионе. Материалы VI Международной научно-практической конференции (Симферополь, 20–22 октября 2011 г.). – Симферополь. – 2011. – С. 63– 68. 26. Костенко Н.С., Дикий Є.О., Заклецький О.А. Просторовий розподіл та зміни донної рослинності Карадазького природного заповідника // Укр. бот. журн. – 2006. – 63, № 2. – С. 243–251. 27. Костенко Н.С., Дикий Е.А., Заклецкий А.А., Марченко В.С. Многолетние 136 изменения в сообществах макрофитобентоса района Карадага (Крым, Черное море) // Морской экологический журнал. Отдельный выпуск. – 2005. – № 1. – С. 48–60. 28. Миронова Л.П., Каменских Л.Н. Сосудистые растения Карадагского заповедника (аннотированный список видов) / Флора и фауна заповедников. – М., ЦНИИТЭИлегпрома, 1995. – Вып. 58. – 102 с. 29. Миронова Л.П., Костенко Н.С., Дідух Я.П., Онищенко В.А., Войцехович А.О. ПЗ Карадазький // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 170–197. 30. Миронова Л.П., Таран Т.А. Состояние раритетного генофонда высших сосудистых растений Карадагского природного заповедника НАН Украины // Флорологія та фітосозологія. Т.1. Збірник наукових праць, присвячених 30-річчю Всеукраїнської секції охорони рослинного світу ім. Б.В. Заверухи Українського товариства охорони природи. – Київ: Фітон. – 2011. – С. 89–102. 31. Миронова Л.П., Шатко В.Г. Популяционное изучение редких растений в Карадагском заповеднике // Редкие виды растений в заповедниках. Сб. науч. тр. ЦНИЛ Главохоты РСФСР. – М., 1987. – С. 95–108. 32. Партика Л.Я. Бріофлора Карадазького заповідника // Укр. ботан. журн. – 1986. – 43, № 3. – С. 26–30. 33. Природа Карадага / М.М. Бескаравайный, Н.С. Костенко, Л.П. Миронова; под ред.: А. Л. Морозова, А. А. Вронский; АН Украинской ССР, Ин-т биологии Южных морей им. А.О. Ковалевского, Карадагский филиал. – Киев: Наукова думка, 1989 . – 286 с. 34. Флора и фауна заповедников. Водоросли, грибы, мохообразные Карадагского заповедника / ред.: В. Е. Соколов, Т. М. Корнеева. – М., 1992. – 65 с. 35. Ходосовцев О.Є. Анотований список лишайників Карадазького природного заповідника // Вісті біосферного заповідника “Асканія-Нова”. – 2003. – Т. 5. – С. 33–45. 36. Шатко В.Г., Миронова Л.П. Состояние популяций некоторых редких растений в Карадагском государственном заповеднике // Бюл. Гл. ботан. сада. – 1986. – Вып. 141. – С. 61–67. Karalarskyi Step V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Караларський степ. Transliteraion/Translaion variants: Karalar Steppe. Area: 10096.0 ha. Altitude: 0–156 m. Latitude: 45°27’07” N (45.4519°). Longitude: 36°12’49” E (36.2135°). Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 2.1%; C – 7.8%; B – 0.4%; D – 0.1%; E – 84.4%; F – 0.2%; H – 4.0%; I – 1.0%. 137 Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.1%; A2 Littoral sediment – 0.1%; A3 Infralittoral rock and other hard substrata – 0.2%; A5 Sublittoral sediment – 1.7%; B1 Coastal dunes and sandy shores – 0.1%; B2 Coastal shingle – 0.2%; B3 Rock clifs, ledges and shores, including the supralittoral – 0.1%; D6 Inland saline and brackish marshes and reedbeds – 0.1%; E1 Dry grasslands – 84.3%; E6 Salt steppes – 0.1%; F3 Temperate and mediterranean-montane scrub – 0.2%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 3.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.3%; I1 Arable land and market gardens – 1.0%. Futher habitat description. A2.1 Litoral coarse sediment; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.4 Sublitoral mixed sediments; B1.2 Sand beaches above the dritline; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; D6.1 Inland saltmarshes; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes (80% of the IPA); E6.2 Continental inland salt steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas, I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – minor, mowing/hay making – minor, nature conservaion and research – major, tourism/recreaion – minor. Protected areas: overlaps (about 6440 ha) with Karalarskyi regional landscape park, includes “Ozero Chokrak” (1000 ha) regional hydrological reserve, overlaps (9885 ha) with Emerald Site (“Karalarskyi”). Threats: development (recreaion/tourism) – low. General description. Major habitat type is the steppe. Dominant species are Sipa brauneri, Sipa pulcherrima, Sipa capillata, Festuca rupicola, Festuca valesiaca, Festuca pseudovina, Bromopsis cappadocica. The largest area is dominated by Sipa brauneri. Typical species are Aegilops cylindrica, Cerastium tauricum, Koeleria cristata, Festuca rupicola, Galatella villosa, Poa bulbosa. On the tops of the ridges, there is the steppe vegetaion dominated by Sipa capillata and co-dominated by Artemisia taurica and Galatella villosa. On the gentle slopes near the inlets, there are the sandy steppes. They are formed by Stipa boryshenica, Carex colchica, Festuca beckeri, Jurinea longifolia. On the calcareous outcrops and screes, there prevail Anisantha tectorum, Alyssum calycocarpum, Ephedra distachya, Euphorbia petrophilla, Poa bulbosa, Pimpinella lithophila. On clay outcrops, there dominate Elytrigia repens, Bromopsis cappadocica, Dactylis glomerata, Poa bulbosa, Medicago minima. On calcareous rocks by the sea, there are Puccinellia distans, Kochia prostrata, Halimione verrucifera, Holosteum umbellatum, Anisantha tectorum, Elytrigia bessarabica. Prevailing species on the sand and shell beach are Leymus sabulosus, Cakile euxina, Crambe pontica. Other typical species of this habitat are Euphorbia peplis, Lactuca tatarica, Pleconax subconica, Salsola kali. subsp. pontica, Xanthium albinum. On the slopes of northern aspects, there is the shrub vegetaion dominated by Crataegus dipyrena, С. monogyna, С. taurica, Prunus spinosa, Rosa spinosissima, Sambucus nigra. There occur Swida australis (Cornus australis), Ligustrum vulgare, Celis glabrata. The herb layer is composed of Arum elongatum, Anthriscus longirostris, Cerasium tauricum, Galium aparine, Rumex euxinus. The IPA includes salt Lake Chokrak (850 ha). The lake is shallow (average 0.85 m). In its litoral, there are communiies of Salicornia perennans, Suaeda prostrata, Spergularia media, Halocnemum strobilaceum, Halimione verrucifera. Botanical significance. One of the largest areas of the steppe vegetaion in Ukraine. Important for two threatned species of Crambe and seaside endemic species Thymus litoralis. Criterion A • Crambe grandilora DC.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Crambe mitridais Juz.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Thymus litoralis Klokov et Shost.; A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 8000 ha; trend: stable; area data quality: medium; trend data quality: medium • F3.247 Ponto-Sarmatic deciduous thickets; area: 15 ha; trend: unknown; area data quality: medium; trend data quality: poor. Literature 1. Дідух Я.П., Шеляг-Сосонко Ю.Р. Ковиловий степ Чигини (Крим) // Укр. ботан. журн. – 1980. – 37, № 4. – С. 79–84. 2. Коломійчук В.П. Флора Караларського регіонального ландшафтного парку (АР Крим) // Укр. ботан. журн. – 2013. – 70, № 3. – С. 326–329. 3. Корженевский В. В., Клюкин А. А. Растительность абразионных и аккумулятивных форм рельефа морских побережий и озер Крыма. – Ялта: ГНБС, 1990. – 108 c. – Деп. в ВИНИТИ 10.07.90, № 3822-В90. 4. Котова И.Н. Флора и растительность Керченского полуострова // Тр. Никит. ботан. сада. Материалы по флоре и растительности Крыма. – 1961. – Т. 35. – С. 64–168. 5. Новосад В.В. Флора Керченско-Таманского региона. – Киев: Наукова думка. – 138 139 1992. – 280 с. 6. Парнікоза І.Ю., Годлевська О.В., Зімнухов Р.О. Шляхи збереження унікальних степових біотопів та археологічної спадщини у Караларському Приазов’ї // Заповідна справа в Україні. – 2010. – Т. 16, вип. 2. – С. 99–104. Kasova Hora V.A. Onyshchenko, N.V. Shumska Ukrainian name: Касова гора. Transliteraion/Translaion variants: Kasova Gora, Kasova Mount, Kasova Hill. Area: 149.7 ha. Altitude: 250–335 m. Latitude: 49°13’17” N (49.2214°). Longitude: 24°42’18” E (24.7048°). Administrative regions. Ivano-Frankivsk region: Halych raion. Ownership: state, private. Biogeographic regions: coninental Habitats. Level 1. E – 96.0%; F – 3.8%; G – 0.2%. Habitats. Level 2. E1 Dry grasslands – 96.0%; F3 Temperate and mediterranean-montane scrub – 3.8%; G1 Broadleaved deciduous woodland – 0.2%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub . Land use: nature conservation and research – major. Protected areas: overlaps (65 ha) with Halytskyi naional nature park, overlaps (65 ha) with 140 Emerald Site “Halytskyi Naional Nature Park”. Threats: abandonment/reducion of land management – medium, agricultural intensification/expansion (grazing) – low, burning of vegetaion – low, development (recreaion/tourism) – low. General description. A hill with the steppe vegetaion. Dominant species are Brachypodium pinnatum, Carex humilis, Elyigia intermedia, Festuca valesiaca, Sipa capillata, Salvia pratensis, Trifolium montanum, Teucrium chamaedrys. Other typical species are Adonis vernalis, Anemone sylvestris, Anthericum ramosum, Asperula cynanchica, Aster amellus, Bupleurum falcatum, Campanula glomerata, Campanula sibirica, Centaurea scabiosa, Chamaecyisus ruthenicus, Filipendula vulgaris, Galium verum, Geranium sanguineum, Inula ensifolia, Inula hirta, Peucedanum cervaria, Prunella grandilora, Salvia pratensis, Salvia vericillata, Thalictrum minus, Veronica spicata. There are gypsum outcrops. A part of the area belongs to the zone of strict protecion of naional park “Halytskyi”. Botanical significance. The largest meadow steppe in Western Ukraine. Important for Carlina cirsioides, Pulsailla grandis and other species of meadow steppes. Criterion A • Carlina cirsioides Klokov; A(iv); abundance: occasional (967 individuals); trend: decreasing; species data quality: good; trend data quality: poor. • Pulsailla grandis Wend.; A(ii); abundance: frequent (10 000 individuals); trend: stable; species data quality: good; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 140 ha; trend: stable; area data quality: good; trend data quality: medium. Literature 1. Куковиця Г.С. Найбільша ділянка ковилового степу на Поділлі // Укр. ботан. журн. – 1970. – 27, № 1. – С. 111–113. 2. Куковиця Г.С., Мовчан Я.І., Соломаха В.А., Шеляг-Сосонко Ю.Р. Синтаксономія лучних степів Західного Поділля // Укр. ботан. журн. – 1994. – 51, № 2–3. – С. 35–48. 3. Куковиця Г.С., Дідух Я.П., Шеляг-Сосонко Ю.Р., Абдулоєва О.С. Синтаксономія лучних степів пам’яток природи республіканського значення гг. Касова та Чортова // Укр. фітоцен. збірн. Серія А. Фітосоціологія. – 1998. – Вип. 2 (11). – С. 42–61. 4. Скоропляс І.О. Сучасний стан популяцій Carlina cirsioides га горі Касова // Вісник Дніпропетровського державного аграрно-економічного університету. – 2014. – 33, № 1. – С. 143–145. 5. Чуй О.В., Шумська Н.В. Поширення видів роду Pulsatilla Mill. у Галицькому національному природному парку та на прилеглих територіях // Рослинний світ у Червоній книзі України: впровадження глобальної стратегії збереження рослин. Матер. Міжнар. наук. конф. (м. Київ, 11–15 жовтня 2010 р.). – К.: Альтерпрес, 2010. – С. 205–209. 6. Шеляг-Сосонко Ю.Р., Дідух Я.П., Єременко Л.П. та ін. Рослинність Касової гори (Опілля) // Укр. ботан. журн. – 1981. – 38, № 3. – С. 60–66. 7. Шумська Н.В., Онищенко В.А., Маланюк В.Б. НПП Галицький // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 105–123. 141 Habitats. Level 1. A – 22.0%; B – 1.4%; E – 67.1%; H – 9.5%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.6%; A2 Littoral sediment – 0.1%; A3 Infralittoral rock and other hard substrata – 8.0%; A5 Sublitoral sediment – 13.3%; B1 Coastal dunes and sandy shores – 0.1%; B2 Coastal shingle – 0.1%; B3 Rock clifs, ledges and shores, including the supralittoral – 1.2%; E1 Dry grasslands – 67.1%; H2 Screes – 0.3%; H3 Inland clifs, rock pavements and outcrops – 9.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. A2.1 Litoral coarse sediment; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.4 Sublitoral mixed sediments; A5.5 Sublitoral macrophyte-dominated sediment; B1.2 Sand beaches above the dritline; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservaion and research – major. Protected areas: includes Kazantypskyi nature reserve (450.1 ha), includes Ramsar Site “Aquaic-clif complex of cape Kazantyp” (251 ha), overlaps (410 ha) with Emerald Site “Kazantypskyi Nature Reserve”. Threats: –. General description. Major habitat type is the stony steppe. It is dominated by Bromopsis cappadocica, Crinitaria villosa, Festuca pseudodalmaica, Festuca pseudovina, Festuca rupicola, Koeleria cristata, Medicago falcata, Sipa capillata, Sipa lessingiana, Sipa ucrainica, Teucrium polium. On the calcareous outcrops, there prevail Anisantha tectorum, Alyssum calycocarpum, Asperula stevenii, Cerasium tauricum, Clypeola jonthlaspi, Ephedra distachya, Euphorbia petrophila, Pimpinella lithophila, Poa bulbosa. On the supralitoral rocks, there is halophytoc vegetaion with dominance of Puccinellia distans, Kochia prostrata, Halimione verrucifera, Holosteum umbellatum, Anisantha tectorum, Elytrigia bessarabica. Major species of the marine vegetaion are Cladophora albida, Cystoseira barbata, Enteromorpha prolifera, Zannichellia major, Zostera nolii (Nanozostera nolii). Botanical significance. Important area for some steppe species, in paricular Allium pervesitum, Crambe grandilora, Crambe grandilora, Crambe mitridais, Crambe pinnaiida. It harbours a small populaion of Ophrys oestrifera outside its main range. One of the most important areas for conservaion of sea-clifs in Ukraine. The best site of the marine vegetaion in the Sea of Azov. Criterion A • Agropyron cimmericum Nevski; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Allium pervesitum Klokov.; A(i), A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Crambe grandilora DC.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe mitridais Juz.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Crambe pinnaiida W.T.Aiton.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Ophrys oestrifera M. Bieb.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • B3.3 Rock cliffs, ledges and shores, with angiosperms; area: 2 ha; trend: stable; area 142 143 Kazantyp V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Казантип. Area: 522.5 ha. Altitude: 0–107 m. Latitude: 45°28’16” N (45.4711°). Longitude: 35°50’36” E (35.8433°). Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. data quality: poor; trend data quality: good. H3.511 Limestone pavements; area: 60 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Исиков В.П., Корнилова Н.В. Казантипский природный заповедник // Сборник тр. Никит. ботан. сада. – 2001. – С. 27–40. 2. Корженевський В.В., Квітницька О.А., Садогурський С.Ю. ПЗ Казантипський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 139–150. 3. Садогурская С.А., Садогурский С.Е., Белич Т.В. Аннотированный список фитобентоса Казантипского природного заповедника Труды Никит. ботан. сада. – 2006. – Т. 126. – С. 190–208. 4. Садогурский С.Е., Белич Т.В. Современное состояние макрофитобентоса Казантипского природного заповедника (Азовское море) // Заповідна справа в Україні. – 2003. – Т. 9, вип 1. – С. 10–15. 5. Ходосовцев А.Е. Аннотированный список лишайников Казантипского природного заповедника // Тр. Никит. ботан. сада. – 2006. – Т. 126. – С. 216–221. • layer and presence of Betula pendula, Dryopteris dilatata, Fagus sylvaica, Luzula luzuloides, Sorbus aucuparia. The moss layer consists of Polytrichum formosum, Pleurozium schreberi, Dicranum scoparium, Bazzania trilobata, Leucobryum juniperoides, Sphagnum spp. Botanical significance. Important area for Pinus cembra forests with Larix polonica. Kedryn R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Кедрин. Area: 225.0 ha. Altitude: 780–1464 m. Latitude: 48°25’09” N (48.4191°). Longitude: 24°01’07” E (24.0187°). Administrative regions. Zakarpatska region: Tiachiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.2%; E – 0.3%; G – 98.6%; H – 0.9%. Habitats. Level 2. C2 Surface running waters – 0.2%; E1 Dry grasslands – 0.3%; G3 Coniferous woodland – 95.6%; G4 Mixed deciduous and coniferous woodland – 3.0%; H2 Screes – 0.5%; H3 Inland cliffs, rock pavements and outcrops – 0.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H2.3 Temperatemontane acid siliceous screes; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – major. Protected areas: includes Kedrynskyi state botanical reserve (166 ha). Threats: climate change/sea level rise – low, forestry (intensiied forest management)) – low. General description. Picea abies (predominantly) and Pinus cembra forests with prevailing of Vaccinium myrillus, Vaccinium viis-idaea, Calamagrosis villosa, Rubus hirtus in the herb 144 Criterion A • Larix decidua Mill. subsp. polonica; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • G3.25 Carpathian Larix and Pinus cembra forests; area: 28 ha; trend: decreasing; area data quality: medium; trend data quality: medium. Conservation proposals. Do not allow clear fellings including sanitary ones. Create an Emerald Site. Expand Kedrynskyi state botanical reserve. Literature 1.Природно-заповідний фонд Закарпатської област. – Ужгород: Карпати, 2011. – 256 с. 2.Стойко С.М., Третяк П.Р., Бойчук І.І. Сосна кедрова (Pinus cembra L.) на верхній межі лісу у Ґорґанах: хорологія, екологія, фенологія // Науковий вісник ДЛГУ: Дослідження, охорона та збагачення біорізноманіття. – Львів: Вид-во ЛДГУ, 1999. – Вип. 99. – С. 173–179. 145 Biogeographic regions: steppic. Habitats. Level 1. C – 0.7%; E – 97.2%; F – 2.0%; G – 0.1%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C2 Surface running waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.5%; E1 Dry grasslands – 96.0%; E2 Mesic grasslands – 1.2%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 0.1%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; F3.2 Submediterranean deciduous thickets and brushes. Land use: agriculture (animals) – minor; mowing/hay making – minor; nature conservaion and research – major. Protected areas: includes division “Khomutovskyi Step” of Ukrainskyi Stepovyi nature reserve (1030.4 ha), overlaps (1030.4 ha) with Emerald Site “Ukrainskyi Stepovyi Nature Reserve”. Threats: abandonment/reducion of land management – low. General description. The area is protected since 1926. Major vegetaion type is the steppe. Dominant species are Poa angusifolia, Elytrigia repens, Elytrigia trichophora, Inula germanica, Vicia tenuifolia, Thalictrum minus, Galatella rossica. Due to the small biomass of herbivores the vegetaion is dominated by bunch grasses (Festuca valesiaca s.l., Sipa capillata, Sipa lessingiana) occupies a lesser area. Typical species are Artemisia austriaca, Artemisia ponica, Caragana frutex, Centaurea adpressa, Euphorbia stepposa, Galium octonarium, Hypericum elegans, Limonium platyphyllum, Linaria vulgaris, Marrubium praecox, Nepeta parvilora, Phlomis pungens, Salvia nutans, Securigera varia, Stachys transsilvanica. Major species of the shrub vegetaion are Rhamnus cathartica, Prunus stepposa, Caragana frutex, Genista scythica. Botanical significance. Important area for conservaion of the steppe vegetaion. Criterion A • Crambe tataria Sebeok.; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Paeonia tenuifolia L.; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1000 ha; trend: stable; area data quality: good; trend data quality: good. Literature 1. Білик Г.І., Осичнюк В.В., Ткаченко В.С. Рослинний покрив Хомутовського степу за даними крупномасштабного картування // Укр. ботан. журн. – 1975. – 32, № 6. – С. 747–752. 2. Білик Г.І., Ткаченко В.С. Рослинний покрив абсолютно заповідної ділянки Хомутовського степу // Укр. ботан. журн. – 1971. – 28, № 3. – С. 337–342. 3. Гелюта В. П., Генов А. П., Ткаченко В. С., Минтер Д. В. Заповедник “Хомутовская степь”. План управления / Под редакцией В. П. Гелюты. – Киев: Академпериодика, 2002. – 40 с. 4. Гринь Ф.О. Заповідник Хомутовський степ // Укр. ботан. журн. – 1956. – 13, № 2. – С. 15–30. 5. Коломійчук В.П., Остапко В.М., Яровий С.С. ПЗ Український степовий // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 336–378. 6. Осичнюк В.В. Зміни рослинності заповідника Хомутовський степ за 40 років // Укр. ботан. журн. – 1966. – 23, № 4. – С. 50–56. 7. Ткаченко В.С. Графічна модель автогенної сукцесії Хомутовського степу // Укр. ботан. журн. – 1992. – 49, № 2. – С. 16–21. 8. Ткаченко В.С. Фітоценотичний моніторинг резерватних сукцесій в Українському степовому природному заповіднику. – К.: Фітосоціоцентр, 2004. – 184 с. 9. Ткаченко В.С., Дідух Я.П., Генов А.П. та ін. Український природний степовий заповідник. Рослинний світ. – К.: Фітосоціоцентр, 1998. – 280 с. 146 147 Khomutovskyi Step V.A. Onyshchenko, V.P. Kolomiychuk Ukrainian name: Хомутовський степ. Transliteraion/Translaion variants: Khomutovskyi Steppe, Homutovsky Steppe. Area: 1059.0 ha. Altitude: 19–71 m. Latitude: 47°17’09” N (47.2857°). Longitude: 38°11’02” E (38.1839°). Administrative regions. Donetsk region: Novoazovsk raion. Ownership: state. Kniazhpilskyi Lis Ukrainian name: Княжпільський ліс. Transliteraion/Translaion variants: Knyazhpil’skyi Forest. Area: 1032.0 ha. Altitude: 150–312 m. Latitude: 48°42’31” N (48.7087°). Longitude: 26°47’15” E (26.7874°). Administrative regions. Khmelnytskyi region: Kamianets-Podilskyi raion. Ownership: state. V.A. Onyshchenko Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – major, nature conservaion and research – major Protected areas: includes Kniazhpilskyi state botanical reserve (821 ha), included in Podilski Tovtry naional nature park, included in Emerald Site “Podilski Tovtry Naional Nature Park”. Threats: –. General description. A wood with the dominance of Quercus robur and Carpinus betulus in the tree layer. In the herb layer, there prevail Carex pilosa, Aegopodium podagraria, Corydalis solida, Anemone ranunculoides. Botanical significance. Important for endemic species Aconitum besserianum. Criterion A • Aconitum besserianum Andrz. ex Trautv.; A(iii); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. Literature 1. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Kolodiazne Biogeographic regions: coninental. Habitats. Level 1. C – 0.5%; E – 0.8%; G – 97.7%; H – 1.0%. Habitats. Level 2. C2 Surface running waters – 0.5%; E2 – Mesic grasslands – 0.8%; G1 Broadleaved deciduous woodland – 96.9%; G3 Coniferous woodland – 0.1%; G4 Mixed deciduous and coniferous woodland – 0.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, V.A. Onyshchenko, M.V. Banik, O.V. Bezrodnova, V.V. Rasevich Ukrainian name: Колодязне. Area: 25.7 ha. Altitude: 119–181 m Latitude: 50°00’57” N (50.0159°). Longitude: 37°39’33” E (37.6592°). Administrative regions. Kharkiv region: Dvorichna raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 58.0%; F – 2.0%; G – 33.0%; H – 7.0%. Habitats. Level 2. E1 Dry grasslands – 58.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 33.0%; H2 Screes – 7.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures . Land use: agriculture (animals) – major; forestry – major. Protected areas: –. Threats: burning of vegetaion – low, extracion (minerals/quarries) – low, forestry (aforestaion) – medium, natural events – low. General description. Slopes of the valley of the Verkhnia Dvorichna river. The broadleaved forest and the steppe vegetaion occupy the largest areas. Besides there are chalk outcrops that are rich in endemic species. Botanical significance. The largest populaion of Daphne sophia in Ukraine. Criterion A • Daphne sophia Kalen.; A(i); A(iv); abundance: 1500 individuals (70% of recorded 148 149 individuals in Ukraine); trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals: Create a state botanical reserve. Literature 1. Banik M. Daphne’04. Final report. – Kharkiv, 2006. – 20 p. (http://www.rufford.org/ files/127.01.04%20Detailed%Final%20Report.pdf). 2. Банік М.В., Тверетинова В.В., Волкова Р.Є., Атемасова Т.А., Атемасов А.А., Брезгунова О.О., Влащенко А.С., Гончаров Г.Л., Коноваленко С.В., Скоробогатов В.М., Скоробогатов Є.В., Целіщев О.Г. Нові місцезнаходження Daphne sophiae Kalen., (Thymeleaceae) в Україні // Укр. ботан. журн. – 2007. – 64, № 4. – С. 565–569. 3. Расевич В.В. Еколого-ценотичні особливості популяцій Daphne sophia Kalen. у природній флорі України // Укр. ботан. журн. – 2008. – 65, № 1. – С. 90–103. 4. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Kolivska Ulohovyna V.A.Onyshchenko Ukrainian name: Колтівська улоговина. Area: 324.0 ha. Altitude: 286–323 m. 150 Latitude: 49°51’20” N (49.8555°). Longitude: 25°06’09” E (25.1026°). Administrative regions. Lviv region: Zolochiv raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 48.0%; E – 40.0%; F – 2.0%; G – 10.0%. Habitats. Level 2. D4 Base-rich fens and calcareous spring mires – 12.0%; D5 Sedge and reedbeds, normally without free-standing water – 36.0%; E3 Seasonally wet and wet grasslands – 39.0%; E5 Woodland fringes and clearings and tall forb stands – 1.0%; F9 Riverine and fen scrubs – 2.0%; G1 Broadleaved deciduous woodland – 10.0%. Futher habitat descripion. D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E2.2 Low and medium altitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tallherb and fern fringes and meadows; F9.2 Salix carr and fen scrub. Land use: mowing/hay making – minor, nature conservation and research – major. Protected areas: same as Verkhniobuzkyi regional landscape reserve, overlaps (about 316 ha) with Pivnichne Podillia naional nature park and Emerald Site “Pivnichne Podillia”. Threats: abandonment/reducion of land management – low. General description. Parially drained mire. It comprises eutrophic reed and sedge communiies, rich fens, wet meadows. The most frequent dominants are Carex appropinquata, Phragmites australis, Carex nigra, Carex lava, Deschampsia cespitosa, Molinia caerulea, Carex rostrata, signiicant area is occupied by communiies of Schoenus ferrugineus and Carex davalliana. 151 In some places there dominate Agrosis stolonifera, Anthoxanthum odoratum, Briza media, Dactylis glomerata, Cladium mariscus, Carex paniculata, Festuca arundinacea, Festuca rubra, Filipendula ulmaria, Scirpus sylvaicus. Other frequent species are Eupatorium cannabinum, Lysimachia vulgaris, Lythrum salicaria, Mentha arvensis, Potenilla erecta. On low elevaions consising of calcareous sand, there are mesic grasslands dominated by Molinia caerulea, Festuca ovina, Calluna vulgaris with Astrania major, Carlina cirsioides, Dracocephalum ruyschiana, Filipendula vulgaris, Genthiane pneumonanthe, Leucanthemum vulgare, Peucedanum oreoselinum, Pimpinella major, Polygonatum odoratum, Prunella grandilora, Pulsailla patens, Serratula inctoria, Stachys oicinalis, Thalictrum minus, Trifolium montanum, Trollius europaeus. Dominants of shrub vegetaion area Salix cinerea and Betula humilis. The tree layer of woods is formed mainly by Betula pubescens. Botanical significance. Important area for Cochlearia polonica, Dracocephalum ruyschiana, Pinguicula bicolor. Criterion A • Cochlearia polonica Frohl.; A(i); A(ii); A(iii); abundance: about 300 individuals (100% of recorded individuals in Ukraine); trend: luctuaing; species data quality: good; trend data quality: good. • Dracocephalum ruyschiana L.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Pinguicula bicolor Woł.; A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Кагало О.О. Фітосозологічна характеристика болотного масиву у верхів’ї р. Західний Буг // Укр. ботан. журн. – 1990. – 47, № 1. – С. 80–84. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 0.3%; E3 Seasonally wet and wet grasslands – 0.0%; F9 Riverine and fen scrubs – 2.0%; G1 Broadleaved deciduous woodland – 25.0%; G3 Coniferous woodland – 66.0%; G4 Mixed deciduous and coniferous woodland – 3.2%; H5 Miscellaneous inland habitats with very Koncha-Zaspivskyi Lis V.A. Onyshchenko Ukrainian name: Конча-Заспівський ліс. Transliteraion/Translaion variants: Koncha-Zaspa Forest. Area: 2376.0 ha. Altitude: 93–123 m. Latitude: 50°16’57” N (50.2826°). Longitude: 30°34’51” E (30.5809°). Administrative regions. Kyiv city: Holosiyivskyi raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. C – 1.7%; D – 0.5%; E – 0.6%; F – 2.0%; G – 94.2%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.9%; C2 Surface running waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.7%; D5 – sedge and reedbeds, normally without free-standing water – 0.8%; E1 Dry grasslands – 0.3%; E2 Mesic grasslands – 152 sparse or no vegetation– 1%. Futher habitat description. E1.1 Inland sand and rock with open vegetation, F9.2 Salix carr and fen scrub, G1.2 Mixed riparian floodplain and gallery woodland, G1.4 Broadleaved swamp woodland not on acid peat, G1.7 Thermophilous deciduous woodland, G1.A Mesoand eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland, G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga, G4.C Mixed Pinus sylvestris – thermophilous Quercus woodland, H5.3 Sparsely- or un-vegetated 153 habitats on mineral substrates not resulting from recent ice activity, H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – major, tourism/recreation – major. Protected areas: includes Lisnyky Botanical Reserve (1110 ha), included in Holosiivskyi national nature park and Emerald Site “Holosiivskyi Naional Nature Park”; Threats: development (recreation/tourism) – low, water (drainage) – medium (urbanization and drainage of adjacent areas). Building cottages on a former mire near the IPA. General description. Forest area in the southern part of Kyiv. The largest porion of this territory is the sand terrace above the floodplain of the Dnipro river with Pinus sylvestris, rarely Quercus robur, forests. The herb layer is dominated by Calamagrostis epigeios, Calamagrostis arundinacea, Festuca ovina, Poa angustifolia. Species of high constancy: Carex ericetorum, Calamagrostis arundinacea, Calamagrostis epigeios, Chamaecytisus ruthenicus, Convallaria majalis, Dicranum polysetum, Euphorbia cyparissias, Festuca ovina, Frangula alnus, Galium verum, Melampyrum pratense, Melica nutans, Peucedanum oreoselinum, Polygonatum odoratum, Pyrus communis, Pleurozium schreberi, Poa angustifolia, Rubus saxatilis, Silene nutans, Sorbus aucuparia, Veronica officinalis. Non-forest vegetaion is represented by sands with vegetaion dominated by Calamagrosis epigeios, Corynephorus canescens, Festuca beckeri, Cladonia miis. In the northwestern part of the site, there is a wide (2 km) valley of a small river. Main vegetation here is mesic and wet forests dominated by Alnus glutinosa, Fraxinus excelsior, Quercus robur, Acer campeste, Tilia cordata, Ulmus minor; Alnus glutinosa and Salix cinerea swamps; eutrophic mires with dominance of Carex riparia, Carex acutiformis, Phragmites australis. Botanical significance. This area contains good examples of diferent forest types. Criterion C • G3.4232 Sarmatic steppe Pinus sylvestris forests; area: 1800 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.21 Riverine Fraxinus – Alnus woodland, wet at high but not at low water; area: 40 ha; trend: stable; area data quality: poor; trend data quality: poor. Conservaion proposals: Do not allow clearcuings including coninuous sanitary fellings. Literature 1. Вірченко В.М. Матеріали до бріофлори НПП “Голосіївський” // Проблеми відтворення і охорони біорізноманіття України. Мат-ли всеукр. наук.-практ. конф. (21– 22 квітня, 2011 р., м. Полтава). – Полтава: Астрая, 2011. – С. 86–88. 2. Дідух Я., Андрієнко Т., Серебряков В., Вольвач Ф., Філенко А., Лопарьов С., Чумак К. Заказник “Лісники” та його проблеми // Ойкумена. – 1994. № 1–2. – С. 116– 127. 3. Дідух Я.П., Чумак К.В., Геоботанічна характеристика заказника “Лісники” (м. Київ) // Укр. ботан. журн. – 1992. – 49. № 3. – С. 22–27. 4. Онищенко В.А., Прядко О.І., Арап Р.Я. НПП “Голосіївський” // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 139–151. 5. Прядко О.І., Арап Р.Я. Поширення та сучасний стан популяцій видів рослин із Червоної книги України на території НПП “Голосіївський” // Мат-ли Міжнародної наукової конференції “Рослинний світ у Червоній книзі України: впровадження Глобальної стратегії збереження рослин”. – Київ, 2010. – С. 297–300. Habitats. Level 2. E1 Dry grasslands – 94.4%; F3 Temperate and mediterranean-montane scrub – 0.5%; G1 Broadleaved deciduous woodland – 2.0%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 0.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 2.1%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; G1.C 154 155 Korsak Mohyla V.A. Onyshchenko, V.P. Kolomiychuk Ukrainian name: Корсак-Могила. Transliteraion/Translaion variants: Korsak Hill. Area: 72.5 ha. Altitude: 87–138 m. Latitude: 46°53’30” N (46.8917°). Longitude: 36°08’06” E (36.1350°). Administrative regions. Zaporizhia region: Prymorsk raion . Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 94.4%; F – 0.5%; G – 2.0%; H – 3.1%. Highly artificial broadleaved deciduous forestry plantations; H2.5 Acid siliceous screes of warm exposures, H3.1 Acid silicious inland clifs; H3.5 Almost bare rock pavements, including limestone pavements; H5.6 Trampled areas. Land use: agriculture (animals) – minor; forestry – minor; nature conservaion and research – major; tourism/recreaion – minor. Protected areas: included in regional landscape reserve “Korsak-Mohyla”, included in Emerald Site “Korsak Mohyla”. Threats: abandonment/reducion of land management – low. General description. Six hills with silicate outcrops. Major habitat type is the steppe dominated by Festuca valesiaca s.l., Sipa capillata, Carex praecox, Caragana frutex, Poa angusifolia, Elytrigia repens, E. intermedia, Bromopsis riparia. On the outcrops, there prevail Achillea leptophylla, Carex praecox, С. stenophylla, Ephedra distachya, Teucrium polium, Thymus dimorphus. Botanical significance. Important area for Caragana scythica in the most transformed region of Ukraine. Criterion A • Caragana scythica (Kom.) Pojark.; A(iv); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Literature 1. Коломійчук В.П. Ботанічна характеристика Корсак-Могили (Запорізька область) // Заповідна справа в Україні. – 2003. – Т. 9, № 1. – С. 1–2. 2. Коломійчук В.П. Psathyrosthachis juncea (Fisch.) Nevski в Северном Приазовье // Вісник Запорізького національного університету: Зб. наук. статей. Фізико-математичні науки. Біологічні науки. – Запоріжжя: ЗДУ. – 2005. – № 1. – С. 100–102. 3. Коломійчук В.П. Ключові ботанічні території Північного Приазов’я // Заповідна справа в Україні. – 2008. – Т. 14, вип. 1. – С. 61–66.Тищенко О.В. Рослинність приморських кіс північного узбережжя Азовського моря. – Київ: Фітосоціоцентр, 2006. – 156 с. Kovalivka O.M. Derkach, H.V. Kolomiets Ukrainian name: Ковалівка. Area: 19.9 ha. Altitude: 5–12 m. Latitude: 47°18’26” N (47.3071°). Longitude: 31°43’01” E (31.7169°). Administrative regions. Mykolaiv region: Mykolaiv raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 59.0%; G – 40.0%; H – 1.0%. Habitats. Level 2. E1 Dry grasslands – 59.0%; G3 Coniferous woodland – 40.0%; H5 Miscellaneous inland habitats with very sparse or no vegetaion – 1.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); G3.F Highly artificial coniferous plantations; H5.6 Trampled areas. Land use: forestry – major. 156 Protected areas: included in regional preserve (zapovidne urochyshche) “Andriivske” Threats: forestry (aforestaion) – medium. General description. A part of sand terrace above the loodplain of the Southern Bug river. Forest plantaions of Pinus pallasiana and Pinus sylvestris in comlex with dry sand grasslands. Dominant species of the grasslands are Carex colchica, Artemisia marschalliana, Festuca beckeri, Koeleria sabuletorum, Thymus pallasianus, Sipa borysthenica. Other frequent species are Scabiosa ucrainica, Achillea ochroleuca, Helichrysum corymbiforme, Astragalus varius, Anchusa gmelinii, Chamaecyisus borysthenicus, Allium savranicum, Jurinea charcoviensis, Tragopogon borysthenicus, Alyssum savranicum. Density of Centaurea margaritalba is 3 to 30 individuals per 100 m2. Botanical significance. A locality of narrow endemic species Centaurea margarita-alba s. str. Criterion A • Centaurea margarita-alba Klokov; A(iii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals: Do not allow aforestaion. Restore sand grasslands in adjacent area. Create a state botanical reserve. Literature 1.Деркач О.М. Ключові ботанічні території Миколаївщини: сучасний стан та проблеми збереження // Теорія і практика заповідної справи в Україні. Зб. наук. праць. – К., 2005. – С. 167–173. 2.Деркач О.М. Андріївське // Південно-Бузький меридіональний екологічний коридор: стислий огляд біорізноманіття та найцінніші території / під ред. В. Костюшина. – К., 2007. – С. 49. 3.Коломієць Г.В. Перлинні волошки секції Pseudophalolepis Klok. ряду Margaritacea Klok. Питання систематики та охорони // Укр. фітоценологічний зб. – Вип. 1–2 (12–13). – К.: Фітосоціоцентр, 1999. – С. 165–169. 4. Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. 157 (Centaurea L.) // Укр. ботан. журн. – 1991. – 48, № 3. – С. 78–80. 5.Крицька Л.І., Деркач О.М., Собко В.Г. Волошка білоперлинна Centaurea margaritaalba Klokov / Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 305. 6.Перлини піщаної флори у пониззях Південного Бугу та Інгулу. Cерія: Збереження біорізноманіття в Приморсько-степовому екокоридорі / Під ред. Г.В. Коломієць. – К.: Громадська організація “Веселий Дельфін”, 2008. – 60 c. typical species are Alyssum minutum, Artemisia marschalliana, Calamagrostis epigeios, Centaurea breviceps, Cerastium schmalhausenii, Cerastium ucrainicum, Dianthus platyodon, Erophila verna, Euphorbia seguieriana, Genista sibirica, Helychrysum corymbiforme, Holosteum umbellatum, Inula sabuletorum, Jurinea laxa, Salix rosmarinifolia, Scabiosa ucrainiaca, Jacobaea borysthenica (Senecio borysthenicus), Thymus borysthenicus, Tragopogon borysthenicus, Veronica arvensis, Veronica dillenii. The layer of mosses and lichens is formed by Tortula ruraliformis, Ceratodon purpureus, Cladonia foliacea, Cladonia rangiformis, Cetraria aculeata, Neofuscelia pockornii. Dominants of mesic grasslands are Agrostis gigantea, Calamagrostis epigeios, Cynodon dactylon, Festuca rupicola, Scirpoides Kozachelaherska Arena V.A. Onyshchenko Ukrainian name: Козачелагерська арена. Transliteraion/Translaion variants: Kozachi Lageri Sands. Area: 18974.0 ha. Altitude: 4–25 m. Latitude: 46°36’07” N (46.6020°). Longitude: 33°03’19” E (33.0552°). Administrative regions. Kherson region: Oleshky (Tsiurupynsk) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.02%; D – 0.07%; E – 25.0%; F – 1.0. G – 24.9%; H – 49.0%. Habitats. Level 2. C1 Surface standing waters – 0.01%; C3 Littoral zone of inland surface waterbodies – 0.01%; D5 Sedge and reedbeds normally without free-standing water – 0.06%; D6 Inland saline and brackish marshes and reedbeds – 0.01%; E1 Dry grasslands – 12.5%; E2 Mesic grasslands – 10.0%; E3 Seasonally wet and wet grasslands – 2.5%; E6 Inland salt steppes – 0.01%; F3 Temperate and mediterranean-mountane scrub – 1.0%; G1 Broadleaved deciduous woodland – 20.9%; G3 Coniferous woodland – 4.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 49.0%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes, E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1), E2.5 Meadows of the steppe zone, E3.4 Moist or wet eutrophic and mesotrophic grassland, F3.1 Temperate thickets and scrub; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia, G3.F Highly artificial coniferous plantations, H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: agriculture (animals) – minor, nature conservation and research – 35%; tourism/ recreation – minor. Protected areas: overlaps (about 6700 ha) with Oleshkivski Pisky national nature park, included in Emerald Site “Oleshkivski Pisky”. Threats: forestry (afforestation) – medium. General description. The largest expanse of unwooded sand in Ukraine. This is a part of the Dnipro river terrace in the steppe zone. Sand dunes reach a height of 5 m. On a large part of the area vegetation is sparse, the most typical species are Agropyron dasyanthum, Chamaecytisus borysthenicus, Linaria dulcis, and non-native species Corynephorus canescens. More dense sand vegetation (sand steppe) is dominated by Festuca beckeri, Koeleria sabuletorum, Agropyron lavrenkoanum, Stipa borysthenica, Carex colchica. Its 158 holoschoenus. Waterlogged habitats are occupied by Carex acutiformis, Carex acuta, Carex riparia, Eupatorium cannabinum, Iris pseudacorus, Juncus conglomeratus, Phragmites australis. Forest vegetation is represented by small (10–2500 m2) natural groves of Betula borysthenica, Populus tremula and small plantations of Pinus sylvestris and Pinus pallasiana. The species composition of Betula borysthenica woods is heterogenous in respect of 159 requirements of species to soil moisture: Agrostis gigantea, Calamagrostis epigeios, Carex elata, Frangula alnus, Genista sibirica, Hieracium umbellatum, Juncus conglomeratus, Phragmites australis, Rhamnus cathartica, Rubus caesius, Salix rosmarinifolia, Solidago virgaurea. Populus tremula woods harbour mainly hygrophilous species Botanical significance. The largest area of unwooded sands in Europe with endemic species. Criterion A • Agropyron dasyanthum Ledeb.; A(i); abundance: frequent; trend: stable; species data quality: medium; trend data quality: poor. • Alyssum savranicum Andrz. (Odontarrhena savranica (Andrz. ex Besser) D.A.German); A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Centaurea breviceps Iljin; A(iii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: good . • X35 Inland sand dunes; area: 13500 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Котенко Т.И., Уманец О.Ю., Селюнина З.В. Природный комплекс Казачьелагерской арены Нижнеднепровских песков и проблемы его сохранения. Сообщение 1. Общая характеристика Казачьелагерской арены // Заповідна справа в Україні. – 1999. – Том 5. Вип. 1. – С. 61–72. 2. Мойсієнко І.І. НПП Олешківські піски // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 357–372. 3. Соломаха І.В., Воробйов Є.О., Мойсієнко І.І. Рослинний покрив лісів та чагарників Північного Причорномор’я. - К.: Фітосоціоцентр, 2015. – 387 с. 4. Уманец О.Ю. Природный комплекс Казачьелагерской арены Нижнеднепровских песков и проблемы его сохранения. Сообщение 2. Изменение флоры и растительности Казачьелагерской арены за 65 лет // Заповідна справа в Україні. – 1999. – Том 5. Вип. 2. – С. 9–15. Habitats. Level 1. E – 50.0%; F – 2.0%; G – 40.0%; H – 8.0%. Habitats. Level 2. E1 Dry grasslands – 50.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 14.0%; G3 Coniferous woodland – 20.0%; G4 Mixed deciduous and coniferous woodland – 6.0%; H2 Screes – 8.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G3.4 Pinus sylvestris woodland south of the taiga; H2.6 Calcareous and ultra-basic screes of warm exposures; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity. Land use: agriculture (animals) – 15%; nature conservaion and research – 85%. Protected areas: overlaps (1134 ha) with Ukrainskyi Stepovyi nature reserve (same as its Kreidiana Flora division), overlaps (1134 ha) with Emerald Site “Ukrainian Steppe Nature Reserve”. V.A. Onyshchenko Ukrainian name: Крейдяна флора. Transliteraion/Translaion variants: Chalk Flora. Area: 1347.0 ha. Altitude: 51–198 m. Latitude: 48°52’07” N (48.8687°). Longitude: 37°53’44” E (37.8956°). Administrative regions. Donetsk region: Sloviansk raion, Lyman (Krasnyi Lyman) raion Ownership: state. Biogeographic regions: steppic. Threats: abandonment/reducion of land management – low. General description. Slopes with outcrops of chalk, tomillares, steppes, oak and pine forests. Chalk with very sparse vegetaion occupies about 20 ha. Open vegetaion on chalk occupies about 100 ha; dominants: Thymus cretaceus, Carex humilis, Festuca valesiaca, Sipa capillata, Jurinea brachycephala, Artemisia salsoloides, Pimpinella itanophila, Botriochloa ischaemum, Koeleria cristata, Koeleria talievii. Dominants of grasslands (about 600 ha): Festuca valesiaca, Poa angusifolia, Sipa capillata; other typical species: Bromopsis riparia, Calamagrosies epigeios, Carex praecox, Elytrigia repens, Euphorbia stepposa, Medicago romanica, Salvia nutans. Prevailing species of shrub vegetaion (about 30 ha): Coinus coggygria, Crataegus curvisepala, Crataegus praearmata, Prunus spinosa, Rhamnus catharica, Rosa corymbifera, Rosa tomentosa, Rosa villosa, Swida sanguinea (Cornus sanguinea). Typical species of Pinus sylvestris woods (about 300 ha) are Quercus robur, Swida sanguinea, Ligustrum vulgare, Coinus coggygria, Rosa canina, Chamaecyisus 160 161 Kreidiana Flora ruthenicus, Euonymus verrucosus, Polygonatum odoratum, Securigera varia, Seseli libaniis subsp. intermedia. Natural broadleaved forests occupies about 150 ha. Their tree layer is dominated by Acer campestre, Acer platanoides, Fraxinus excelsior, Quercus robur, Tilia cordata, Ulmus minor. In the herb layer, there dominates Aegonychon purpureo-coeruleum, Dactylis glomerata, Elytrigia intermedia, Melica picta, Stellaria holostea. Area of broadleaved forest is increasing. Botanical significance. Important area for conservaion of chalk outcrops with endemic endemic species and termophilous broad-leaved forests. Criterion A • Alyssum gymnopodum P.Smirn. (Odontarrhena gymnopoda (P.A.Smirn.) D.A.German); A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Diplotaxis cretacea Kotov; A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Linaria cretacea Fisch. ex Spreng.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Silene cretacea Fisch. ex Spreng.; A(ii), A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Sipa zalesskii Wilensky; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Syrenia talievi Klokov; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E1.13 Coninental dry rocky steppic grasslands and dwarf scrub on chalk outcrops; area: 200 ha; trend: increasing; area data quality: medium; trend data quality: good. • F3.247 Ponto-Sarmatic deciduous thickets; area: 36 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.7 Thermophilous deciduous woodland (*91I0); area: 200 ha; trend: increasing; area data quality: medium; trend data quality: good. Literature 1. Ткаченко В.С., Генов А.П. Мовчан Я.І. Флористична характеристика Криволуцького кретофільного степу на Донбасі та необхідність його заповідання // Укр. ботан. журн. – 1987. – 44, № 4. – С. 70–75. 2. Ткаченко В.С., Дідух Я.П., Генов А.П. та ін. Український природний степовий заповідник. Рослинний світ. – К.: Фітосоціоцентр, 1998. – 280 с. 3. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Kreidiani Vidslonennia Ukrainian name: Крейдяні відслонення. Transliteraion/Translaion variants: Chalk Outcrops. Area: 43.8 ha. Altitude: 90–110 m. Latitude: 49°19’00” N (49.3167°). 162 V.A. Onyshchenko Longitude: 39°49’55” E (39.8320°). Administrative regions. Luhansk region: Milove raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 84.0%; H – 16.0%. Habitats. Level 2. E1 Dry grasslands – 83.0%; E6 Salt steppes – 1.0%; H2 Screes – 16.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E6.2 Continental inland salt steppes, H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; nature conservaion and research – major. Protected areas: includes Kreidiani Vidslonennia regional botanical reserve (30 ha), includes Emerald Site “Kreidiani Vidslonennia” (30 ha). Threats: agricultural intensification/expansion (arable) – low, extracion (minerals/quarries) – low; forestry (aforestaion) – low. General description. Slope of the valley of the Komyshna river with the steppe vegetaion and outcrops of chalk. Major dominants of the steppe vegetaion are Festuca valesiaca and Sipa capillata. On the tops of the hills, there are psammophyic steppes dominated by Festuca beckeri and Cleistogenes squarrosa. Prevailing dominant on the chalk outcrops is Thymus calcareus. Minor dominants are Artemisia hololeuca, Artemisia salsoloides, Hyssopus cretaceus, Linaria cretacea, Onosma tanaiica, Pimpinella itanophila, Scrophularia cretacea. Botanical significance. Important area for conservaion of Hedysarum cretaceum and other endemic species of chalk outcrops. Criterion A 163 • Hedysarum cretaceum J.Gay.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Literature 1. Природно-заповідний фонд Луганської області // О.А. Арапов (заг. ред.), Т.B. Сова, О.А. Cавенко, В.Б. Фєрєнц, Н.У. Кравець, Л.Л. Зятьков, Л.О. Морозова. Довідник. – 3-е вид., доп. і перероб. – Луганськ: “Луганська правда”, 2013. – 224 с. Kremenchutski Plavni expansion (grazing) – low. General description. The area includes parts of the loodplains of the Dnipro and Psel rivers. A large area is covered by riverine Populus alba, Populus nigra, Salix alba woods, meadows with dominance of Poa pratensis, Agrosis stolonifera, Elytrigia repens, psammophyic grasslands dominated by Koeleria glauca s.l., Festuca beckeri, Calamagrosis epigerios, Artemisia campestris s.l., loodplain Quercus robur woods and swamped Alnus gluinosa woods with herb layer of Carex riparia and Carex acuiformis. Litoral communiies are dominated by Typha angusifolia, Typha laifolia, Phragmites australis. Major dominants of aquaic vegetaion are Certophyllum demersum, Ceratophyllum submersum, Lemna minor, Myriophyllum spicatum, Potamogeton lucens, Potamogeton crispus, Hydrocharis morsusranae, Nuphar lutea, Trapa borysthenica. V.A. Onyshchenko Ukrainian name: Кременчуцькі плавні. Transliteraion/Translaion variants: Kremenchuk Wetlands. Area: 7231 ha. Altitude: 64–70 m. Latitude: 49°02’59” N (49.0496°). Longitude: 33°26’49” E (33.4468°). Administrative regions. Poltava region: Horishni Plavni (Komsomolsk) city, Kremenchuk city, Kremenchuk raion. Ownership: state. Biogeographic regions: continental Habitats. Level 1. C – 20%; D – 10%; E – 31%; F – 4%; G – 35%. Habitats. Level 2. C1 Surface standing waters – 5%; C2 Surface running waters – 10%; C3 Littoral zone of inland surface waterbodies – 5%; D5 Sedge and reedbeds, normally without free-standing water – 10%; E1 Dry grasslands – 1%; E2 Mesic grasslands – 15%; E3 Seasonally wet and wet grasslands – 14%; E5 Woodland fringes and clearings and tall forb stands – 1%; F9 Riverine and fen scrubs – 4%; G1 Broadleaved deciduous woodland – 34%; G3 Coniferous woodland – 1%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.5 Periodically inundated shores with pioneer and ephemeral vegetation; C3.6 Unvegetated or sparsely vegetated shores with soft or mobile sediments; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.3 Mediterranean riparian woodland; G1.4 Broadleaved swamp woodland not on acid peat. Land use: agriculture (animals) – minor, conservation and research – major, forestry – 30%; mowing / hay making – major, urban/industrial/transport – minor. Protected areas: includes Biletskivski Plavni state landscape reserve (2980 ha), includes Kremenchutski Plavni regional landscape park (5080 ha), includes Emerald Site “Kremenchutski Plavni Regional Landscape Park” (5080 ha), overlaps with Emerald Site “Dniprodzerzhynske Reservoir” (290 ha). Threats: abandonment/reduction of land management – low; agricultural intensification/ Botanical significance. The area is noted for conservaion of comlexes of a big river (forests, shrubs, litoral and aquaic vegetaion, meadows). Criterion C • E3.4 Moist or wet eutropic and mesotrophic grassland; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: medium. • F9.1 Riverine scrub; area: 500 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.11 Riverine Salix woodland; area: 300 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.3 Mediterranean riparian woodland; area: 1800 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Водно-болотні угіддя України. Довідник / Під ред. Марушевського Г.Б., Жарук І.С. – К.: Чорноморська програма Ветландс Интернешнл, 2006. – 312 с. 2. Гальченко Н. П. Рослинність регіонального ландшафтного парку “Кременчуцькі плавні” // Укр. ботан. журн. – 2004. – 61, № 4. – С. 48–55. 3. Гальченко Н.П. Регіональний ландшафтний парк “Кременчуцькі плавні” / Природнозаповідні території України. Рослинний світ. – Вип. 5. – К.: Фітосоціоцентр, 2006. – 176 с. 164 165 Habitats. Level 1. A – 0.1%; B – 0.0%; C – 0.0%; E – 13.0%; F – 3.0%; G – 82.9%; H – 1.0%; J – 0.0%. Habitats. Level 2. A1 Littoral rock and other hard substrata sediment – 0.0%; A2 Littoral sediment – 0.1%; A3 Infralittoral rock and other hard substrata sediment – 0.1%; A5 Sublittoral sediment – 0.0%; B2 Coastal shingle – 0.0%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.0%; C1 Surface standing waters – 0.0%; C2 Surface running waters – 0.0%; C3 Littoral zone of inland surface waterbodies – 0.0%; E1 Dry grasslands – 11.0%; E2 – Mesic grasslands – 2.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; F5 – Maquis, arborescent matorral and thermo-Mediterraneal brushes; F6 – Garrigues; F7 Spiny Mediterranean heaths – 1.0%; G1 Broadleaved deciduous woodland – 77.3%; G3 Coniferous woodland – 3.0%; G4 Mixed deciduous and coniferous woodland – 2.6%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 0.8%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.1 Litoral coarse sediment; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.5 Sublitoral macrophyte-dominated sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetaion; E1.2 Perennial calcareous grassland and basic steppes; E1.3 Mediterranean xeric grassland; E2.5 Meadows of the steppe zone; F3.2 Submediterranean deciduous thickets and brushes; F5.2 Maquis; F5.3 Pseudomaquis; F6.4 Black Sea garrigues; F7.4 Hedgehog-heaths; G1.6 Fagus woodland; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.5 Pinus nigra woodland; G3.7 Lowland to montane mediterranean Pinus woodland (excluding Pinus nigra); G3.F Highly ariicial coniferous forestry plantaions; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resuling from recent ice acivity; H5.6 Trampled areas. Land use: agriculture (animals) – 3%; forestry – 65%; nature conservaion and research – 28%; tourism/recreaion – major. Protected areas. Naional: overlaps (34563 ha) with Krymskyi nature reserve (includes mountain part of the reserve), includes Yaltynskyi Hirsko-Lisovyi nature reserve (14523 ha), includes Aharmyskyi Lis state complex nature monument (40 ha), overlaps (17954 ha) with Baydarskyi state landscape reserve, includes Dolhorukivska Yayla regional landscape reserve (2130 ha), includes Hirskyi Karst Krymu state geological reserve (4316 ha), includes Hirskyi Masyv Karaul-Oba state compex nature monument (100 ha), includes Hora Kara-Tau state botanical nature monument (100 ha), includes Kachynskyi Kanyon state geological reserve (100 ha), includes Karabi-Yaylynska Ulohovyna state botanical nature monument (32 ha), includes Karstova Shakhta Soldatska state geological nature monument (10 ha), includes Khapkhalskyi state hydrological reserve (250 ha), includes Kyzyl-Koba state geological nature monument (33 ha), includes Manhup-Kale state complex nature monument (90 ha), includes Mys Aia state landscape reserve (1340 ha), includes Novyi Svit state botanical reserve (477 ha), includes Urochyshche Demerdzhi state geological nature monument (20 ha), includes Urochyshche Karabi-Yayla state bonaical reserve (491 ha), includes Urochyshche Karasu-Bashi state hydrological nature monument (24 ha), includes Urochyshche Kubalach state bonaical reserve (526 ha), includes Velyky Kanyon Krymu state landscape reserve (300 ha). Regional: includes Ai-Petrynska Yayla regional landscape reserve (1795 ha), includes Ai-Serez regional complex nature monument (5 ha), includes Bakla regional geological nature monument (5 ha), includes Belbetskyi Tysovyi Hay regional botanical reserve (20 ha), includes Demerdzhi Yayla regional landscape reserve (2076 ha), includes regional reserve “Dolyna Richky Satera” (10 ha), includes regional reserve “Hirsko-Lisovyi Masyv Bilia Sela Topolivka I Sela Kurske” (20 ha), includes Hora Koshka regional complex nature monument (50 ha), includes Hora Krestova regional complex nature monument (7 ha), includes regional botanical reserve Karabi-Yayla (2829 ha), includes Papaya-Kaya regional landscape reserve (550 ha), includes Hora Liagushka regional complex nature monument (5 ha), includes regional geological nature monument “Pryrodni Sinksy Karalezkoyi Dolyny” (5 ha), includes regional geological nature monument 166 167 Krymski Hory V.A. Onyshchenko Ukrainian name: Кримські гори. Transliteraion/Translaion variants: Crimean Mountains. Area: 301150.0 ha. Altitude: 0–1545 m. Latitude: 44°45’07” N (44.7520°). Longitude: 34°15’17” E (34.2548°). Administrative regions. Autonomous Republic of Crimea: Alushta city, Bakhchysarai raion, Bilohirsk raion, Feodosia city, Kirovske raion, Simferopol raion, Sudak city, Yalta city. Sevastopol city: Balaklava raion. Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. “Pryrodni Sinksy v Dolyni Richky Churuk-Su” (5 ha), includes Skeli Laspi regional preserve (18 ha), includes Tepe-Kermen regional geological nature monument (5 ha), includes Urochyshche Parahilmen regional botanical reserve (225 ha), includes regional landscape park “Nauchnyi” (965 ha). Internaional: overlaps (22117 ha) with Emerald Site “Baidarskyi ta Mys Aia”, overlaps (42597 ha) with Emerald Site “Bakhchysaraisko-Alushtynskyi”, includes (130603 ha) Emerald Site “Bilohirskyi”, overlaps (34563 ha) with Emerald Site “Crimean Nature Reserve”, overlaps (3651 ha) with Emerald Site “Sevastopolskyi”, includes Emerald Site “Yaltynskyi Hirsko-Lisovyi Nature Reserve” (14523 ha), includes Emerald Site “Gora Bila” (1091 ha). Threats: burning of vegetaion – medium, development (recreaion/tourism) – low, development (urbanizaion) – low, eutrophicaion – low. General description. IPA includes major part of the Crimean mounains. Flora and vegetaion are of Eastern submediterranean type with steppe elements. Forest vegetaion occupies the largest area. Besides there are a lot of steppe vegetaion and large (>100 meters in height and several kilometers in length) limestone clifs. Major forest type is mesic Quercus petraea, Carpinus betulus and Fraxinus excelsior forests with Cornus mas in the shrub layer and dominance of Mercurialis perennis, Physospermum cornubiense, Ranunculus constaninopolitanus in the herb layer. At lower alitudes, there are Quercus pubescens and Carpinus orientalis woods with high paricipaion of Aegonychon purpureo-caeruleum, Carex hallerana, in drier habitats – open Quercus pubescens woods dominated by Elytrigia nodosa. Fagus sylvaica ssp. moesiaca forests prevails at alitudes above 700 m. In their herb layer, Dentaria glandulosa, Galium odoratum, Mercurialis perennis dominates. In the lower belt, there occur Juniperus excelsa woodlands with paricipaion of Arbutus andrachne, Cistus tauricus, Jasmnum fruicans, Juniperus oxycedrus, Quercus pubescens. In the layer of herbs and low shrubs, there dominate of Achnatherum bromoides, Bromopsis cappadocica, Elytrigia nodosa, Festuca callieri, Helianthemum stevenii, Poa sterilis, Thymus callieri, Teucrium chamaedrys. On the southern slope of the main mountain chain, near Yalta city, a considerable area is occupied by Pinus pallasiana (P. nigra ssp. pallasiana) and Pinus sylvestris var. hamata (Pinus kochiana) forests with dominance of Brachypodium rupestre, Carex humilis, Laser trilobum, Pteridium aquilinum. Besides there occur Acer stevenii, Alnus gluinosa, Pinus bruia woods. Steppe vegetaion occupies large areas on the tops of mountains (“Yayla”) and at low alitudes in outer parts of the mountains. Dominants of the steppe vegetaion are Agropyron ponicum, Bromopsis cappadocica, Carex humilis, Elytrigia nodosa, Festuca valesiaca, Sipa brauneri, Sipa lithophila, Sipa ponica, Sipa irsa, Sipa pulcherrima. Mesic grasslands occur in medium and upper belts. Tomillares are in all belts. Maximum of their distribuion is on Yayla. Dominaing species are Asphodeline taurica, Helianthemum stevenii, Teucrium chamaedrys, Teucrium jailae, Thymus callieri, Thymus hirsutus, Tymus tauricus. Botanical significance. This area is important for a large number of species and habitats. For some threatened species it includes all their extent of occurence. Criterion A • Astracantha arnacantha (M.Bieb.) Podlech; A(iv); abundance: frequent; trend: decreasing; species data quality: good; trend data quality: poor. • Astragalus setosulus Gontsch.; A(i), A(ii), A(iii); abundance: rare; trend: decreasing; species data quality: medium; trend data quality: poor. • Centaurea comperiana Steven; A(iii); abundance: occasional; trend: unknown; species data quality: poor; trend data quality: poor. • Centaurea sarandinakiae N.B.Illar.; A(iv); abundance: rare; trend: unknown; species 168 • • • • • • • • • • • • • • • • • • • • • • • data quality: medium; trend data quality: poor. Cephalaria demetrii Bobrov; A(iii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Chamaecyisus wulii (V.Krecz.) Klásková; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Comperia comperiana (Steven) Asch. et Graebn.; A(ii); abundance: occasional; trend: decreasing; species data quality: medium; trend data quality: poor. Cyclamen kuznetzovii Kotov et Czernowa.; A(ii); A(iii); abundance: occasional (>10 000 000 individuals, area of occupancy 400 ha); trend: stable; species data quality: good; trend data quality: poor. Cypripedium calceolus L.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Daphne taurica Kotov.; A(iii); abundance: 256 individuals (two localiies); trend: stable; species data quality: good; trend data quality: medium. Eremurus tauricus Steven; abundance: A(iv); occasional; trend: unknown; species data quality: medium; trend data quality: poor. Himantoglossum caprinum (Bieb.) C.Koch.; A(ii), A(iv); abundance: occasional; trend: decreasing; species data quality: medium; trend data quality: medium. Lagoseris purpurea (Willd.) Boiss.; A(i), A(ii), A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Medicago saxailis M.Bieb.; A(i); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Onobrychis pallasii (Willd.) M.Bieb.; A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Onosma polyphylla Ledeb.; A(ii), A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Ophrys oestrifera Bieb.; A(ii); abundance: occasional; trend: decreasing; species data quality: medium; trend data quality: poor. Ophrys taurica (Aggeenko) Nevski Bieb.; A(ii); abundance: occasional; trend: decreasing; species data quality: medium; trend data quality: poor. Orchis provincialis Balb.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Orchis punctulata Steven ex Lindl.; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Paeonia tenuifolia L.; abundance: A(ii); frequent (1 000 000 individuals); trend: unknown; species data quality: good; trend data quality: poor. Pinus stankewiczii (Sukacz.) Fomin (P. bruia Ten. var. pityusa (Steven) Silba; A(i), A(iv); abundance: occasional (three natural localiies with high number of individuals); trend: decreasing; species data quality: good; trend data quality: medium. Rhus coriaria L.; A(i); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. Silene jailensis N.I.Rubtzov; A(iii); abundance: 470 individuals (in 4 localiies); trend: stable; species data quality: medium; trend data quality: poor. Sisymbrium confertum Steven ex Turcz.; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Steveniella satyrioides (Steven) Schlechter; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Tilia dasystyla Stev.; A(iv); abundance: occasional; trend: stable; species data quality: 169 medium; trend data quality: poor. Criterion B • G1 Broadleaved deciduous woodland; area 240 000 ha; % of indicator species: 54.5%; No of indicator species: 42; trend: stable; species data quality: good; area data quality: good; trend data quality: good. Criterion C • B3.3 Rock cliffs, ledges and shores, with angiosperms; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. • C2.12 Hard water springs; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 27 000 ha; trend: stable; area data quality: medium; trend data quality: medium. • F3.247 Ponto-Sarmatic deciduous thickets; area: 5000 ha; trend: stable; area data quality: poor; trend data quality: medium. • F7 Spiny Mediterranean heaths; area: 800 ha; trend: stable; area data quality: poor; trend data quality: medium. • G1.A4 Ravine and slope woodland; area: 100 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.6 Fagus woodland (excluding G1.66); area: 40000 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.7 Thermophilous deciduous woodland; area: 40000 ha; trend: stable; area data quality: medium; trend data quality: medium. • G3.4E Ponto-Caucasian Pinus sylvestris forests; area: 2000 ha; trend: decreasing; area data quality: medium; trend data quality: medium. • G3.5 Pinus nigra woodland; area: 9000 ha; trend: decreasing; area data quality: medium; trend data quality: good. • G3.7 Lowland to montainmediterranean Pinus woodland (excluding Pinus nigra); area: 200 ha; trend: decreasing; area data quality: medium; trend data quality: medium. • G3.9 Coniferous woodland dominated by Cupressaceae or Taxaceae; area: 5000 ha; trend: decreasing; area data quality: medium; trend data quality: good. • H2.6 Calcareous and ultra-basic screes of warm exposures; area: 3000 ha; trend: stable; area data quality: poor; trend data quality: medium. • H3.2 Basic and ultra-basic inland cliffs; area: 15 000 ha; trend: stable; area data quality: medium; trend data quality: good. • H3.511 Limestone pavements; area: 5000 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Didukh Ya.P. The communities of the class Quercetea pubescenti-petraeae at the Crimean Mountains // Ukr. Phytosoc. Col. – Kyiv, 1996. – Ser. A., iss. 1. – P. 63–77. 2. Korzhenevsky V.V. Pinus pallasiana forest in the Crimea // Укр. фiтосоцiол. збiрник. – Київ, 1998. – Сер. А. № 1 (9). – С. 78–97. 3. Дідух Я.П. Томіляри Гірського Криму // Укр. бот. журн. – 1981. – 38, № 4. – С. 84–89. 4. Дидух Я.П. Опыт класификации ксерофильной полукустарниковой и травянистой растительности Горного Крыма // Ботан. журн., 1983. – 68, № 11. – С. 1456–1466. 5. Дидух Я.П. Растительный покров Горного Крыма (структура, динамика, эволюция и охрана). – Киев: Наукова думка, 1992 – 256 с. 6. Дідух Я.П. Неморальні ліси Гірського Криму класу Querco-Fagetea Br.-Bl. еt. Vlieg. 1937 // Український фітоценологічний збірник, 1996. – Сер. А, №3. – С. 34–51. 7. Дідух Я.П. Гірські бори (Erico-Pinetea Horvat 1959) України // Рослинність хвойних лісів України. – К., 2003. С. 43–79. 8. Дідух Я.П., Куземко А.А. Нові синтаксони класу Molinio-Arrhenatheretea з Гірського Криму // Чорноморський ботан. журн. – 2009. – 5, № 4. – С. 547–562. 9. Дідух Я.П. ПЗ Ялтинський гірсько-лісовий // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 390–405. 10. Зелена книга України / під ред. Я.П. Дідуха – К.: Альтерпрес, 2009. – 448 с. 11. Корженевский В.В. Сосняки из Pinus kochiana на Главной гряде Крымских гор (синтаксономическое положение) // Классификация растительности СССР (с использованием флористических критериев). М.: Изд-во Моск. ун-та, 1986. – С. 102–112. 12. Корженевський В.В., Киселев О.А. Фитоценология восточно-буковых лесов южного макросклона Главной гряды Крымских гор // Структура растительности и биоэкология растений Крыма. – Ялта, 1982. – С. 26–35. 13. Корженевський В.В., Руденко М.І., Садогурський С.Ю. ПЗ Кримський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 198–220. 14. Партика Л.Я. Бріофлора Ялтинського гірсько-лісового природного заповідника // Укр. ботан. журн. – 1995. – 52, № 2. – С. 260–270. 15. Ходосовцев О.Є., Богдан О.В. Анотований список лишайників Ялтинського гірсько-лісового заповідника // Чорноморський ботан. журн. – 2005. – 1. – С. 117–132. 16. Рифф Л.Е. Продромус рослинності кам’янистих відслонень Гірського Криму // Ю.Д. Клеопов та сучасна ботанічна наука. – К: Фітосоціоцентр, 2002. – С. 286–289. 17. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 170 171 Kuchuhury V.P. Kolomiychuk Ukrainian name: Кучугури. Transliteraion/Translaion variants: Kuchugury. Area: 75.8 ha. Altitude: 13–21 m. Latitude: 47°32’47” N (47.5463°). Longitude: 35°12’18” E (35.2049°). Administrative regions. Zaporizhia region: Vasylivka raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 40.0%; E – 30.0%; F – 7.0%; G – 18.0%; H – 5.0%. Habitats. Level 2. C1 Surface standing waters – 30.0%; C3 Littoral zone of inland surface waterbodies – 10.0%; E1 Dry grasslands – 30.0%; F3 Temperate and mediterraneanmontane scrub – 3.0%; F9 Riverine and fen scrubs – 4.0%; G1 Broadleaved deciduous woodland – 18.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 5.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); F3.1 Temperate thickets and scrub; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity. Land use: nature conservaion and research – 100%. Protected areas: included in Velyky Luh naional nature park (zone of strict protecion); included in Emerald Site “Velykyi Luh Naional Nature Park”. Botanical significance. one of two known locality of narrow endemic species Centaurea konkae. Criterion A • Centaurea konkae Klokov; A(iii); abundance: occasional (900 individuals); trend: unknown; species data quality: good; trend data quality: poor. Literature 1. Коломійчук В.П. Сучасний список регіонально рідкісних судинних рослин Запорізької області // Промышленная ботаника. – 2011. – Вып. 11. – С. 105‒111. 2. Коломійчук В.П., Гальченко Н.П. Національний природний парк Великий Луг // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 63–76. 3. Тарасов В.В. Флора Дніпропетровської та Запорізької областей. Судинні рослини. – Д.: Вид-во ДНУ, 2005. – 276 с. 4. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Kuchurhan Threats: natural events – low (erosion of islands). General description. Sand islands in the Khakovka resrvoir. Dry sand grasslands are dominated by Artemisia marschalliana and Secale sylvestre. Species of signiicant constancy: Achillea micrantha, Agropyron dasyanthum, Carex colchica, Chondrilla juncea, Euphorbia seguieriana, Jurinea paczoskiana, Rumex acetosella, Linaria odora subsp. dulcis, Jacobaea borysthenica, Seseli tortuosum. Total cover is 50–80%. Besides there are Salix alba woods, Salix acuifolia scrub and fresh standing waters with aquaic vegetaion and litoral Phragmites australis communiies. 172 V.A. Onyshchenko, O.M. Popova Ukrainian name: Кучурган. Transliteraion/Translaion variants: Kuchurgan. Area: 1673 ha. Altitude: 21–160 m. Latitude: 46°57’29” N (46.9580°). Longitude: 29°53’28” E (29.8909°). Administrative regions. Odesa region: Rozdilna raion, Velyka Mykhailivka raion Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 65.0%; F – 2.0%; G – 32.0%; H – 1.0%. Habitats. Level 2. E1 Dry grasslands – 63.0%; E2 Mesic grasslands – 2.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 17.0%; G3 Coniferous woodland – 15.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations; H5.6 Trampled areas. Land use: agriculture (animals) – 70%; forestry – 24%; mowing/hay making – minor Protected areas: same as Emerald Site “Kuchurhanskyi”. Threats: forestry (aforestaion) – medium. General description. Eroded slopes of the Kuchurgan valley and its right tributary. The largest area is occupied by steppe vegetaion and forest plantaions. No detailed data on vegetaion. Botanical significance. Important for conservaion of Colchicum fominii (~Colchicum 173 Habitats. Level 1. E – 94.0%; F – 2.0%; G – 2.0%; H – 2.0%. Habitats. Level 2. E1 Dry grasslands – 94.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 0.4%; G3 Coniferous woodland – 1.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 2.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); F3.1 Temperate thickets and scrub; G3.F Highly artificial coniferous plantations; H5.6 Trampled areas. Land use: forestry – 100%. Protected areas: included in Emerald Site “Dniprovske Reservoir”. Threats: forestry (aforestaion) – high, burning of vegetaion – low. General description. IPA is situaued on the sand terrace of the Dnipro river. Major vegenaion type is the dry sand grasslands dominated by Festuca beckeri, Artemisia marschalliana, Secale sylvestre with total cover 40–50%. Frequent species are Achillea micrantha, Agropyron dasyanthum, Carex colchica, Chondrilla juncea, Euphorbia seguieriana, Jurinea charkoviensis, Rumex acetosella, Linaria odora subsp. dulcis, Jacobaea borysthenica, Seseli tortuosum. With lower constancies, there occur Astragalus varius, Anchusa gmelinii, Chamaecyisus borysthenicus, Gypsophilla paniculata. Populaion of Centaurea konkae occupies about 1 ha. It has several hundred individuals. Botanical significance. One of two known populaion of narrow endemic species Centaurea konkae. arenarium) in Ukraine. Criterion A • Colchicum fominii Bordz.; A(ii), A (iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals: Do not allow ariicial aforestaion, restore natural vegetaion. Kurylivka Ukrainian name: Курилівка. Area: 65.4 ha. Altitude: 55–58 m. Latitude: 48°33’24” N (48.5566°). Longitude: 34°37’19” E (34.6220°). Administrative regions. Dnipropetrovsk region: Petrykivka raion. Ownership: state. Biogeographic regions: steppic. 174 V.P. Kolomiychuk Criterion A • Centaurea konkae Klokov; A(iii); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals: Create a state botanical reserve. 175 Literature 1. Тарасов В.В. Флора Дніпропетровської та Запорізької областей. Судинні рослини. – Дніпропетровськ: Вид-во ДНУ, 2005. – 276 с. 2. Червона книга Дніпропетровської області. (Рослинний світ) / Під ред. А.П. Травлєєва. – Дніпропетровськ: ВКК “Баланс-Клуб”, 2010. – 500 с. 3. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. persicifolia, Centaurea pseudophrygia, Clinopodium vulgare, Maianthemum bifolium, Meliis sarmaica, Polygonatum odaratum, Potenilla alba, Primula veris, Pulsatilla patens, Serratula coronata. In the herb layer of Alnus gluinosa woods, there dominate Carex vesicaria, Scirpus sylvaicus. Constant species are Carex acuiformis, C. elongata, С. rostrata, Galium uliginosum, Juncus conglomeratus, Lysimachia vulgaris, Lythrum salicaria, Padus racemosa, Peucedanum palustre, Poa palustris. Prevailing species of meadows are Arrhenatherum elaius, Carex panicea, Cynosurus cristatus, Festuca rubra. Levkivski Lisy O.O. Orlov Ukrainian name: Левківські ліси. Transliteraion/Translaion variants: Levkivsky Forest. Area: 973.0 ha. Altitude: 176–201 m. Latitude: 50°13’36” N (50.2265°). Longitude: 28°53’56” E (28.8987°). Administrative regions. Zhytomyr region: Zhytomyr raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.3%; E – 0.2%; G – 98.5%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.2%; C3 Littoral zone of inland surface waterbodies – 0.1%; E2 Mesic grasslands – 0.2%; G1 Broadleaved deciduous woodland – 9.5%; G3 Coniferous woodland – 14.5%; G4 Mixed deciduous and coniferous woodland – 60.0%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, earlystage woodland and coppice – 14.5%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. E2.2 Low and medium alitude hay meadows; G1.7 Thermophilous deciduous woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H5.6 Trampled areas. Land use: forestry – major. Protected areas: included in Emerald Site “Korostyshivskyi”. Threats: forestry (intensiied forest management) – medium. General description. Vegetaion is represented mainly by forests (deciduous, mixed and coniferous approximately in equal parts). Mesic Pinus sylvestris forests are dominated by Peucedanum oreoselinum, Dicranum polysetum, Pleurozium schreberi. Other frequnt species are Campanula rotundifolia, Chamaecyisus ruthenicus, Dianthus pseudosquarrosus, Gypsophila fasigiata, Luzula pilosa, Melampyrum pratense, Pulsatilla patens, Rumex acetosella, Thymus serpyllum, Vaccinium viis-idaea. In weter pine forests, dominant species of the lower layers are Frangula alnus, Vaccinium myrillus, Molinia caerulea, Pteridium aquilinum, Dicranum polysetum, Pleurozium schreberi. Secondary Betula pendula woods have species composiion similar to one of pine woods. Dominants of the herb layer of Quercus robur woods and mixed Pinus sylvestris - Quercus robur woods are Convallaria majalis and Pteridium aquilinum. Their constant species are Betonica oicinalis, Campanula 176 Botanical significance. Large dense populaion of Pulsailla patens. One of the largest known localiies of endemic species Dianthus pseudoseroinus. A good example of species rich oak woods. Criterion A • Dianthus pseudoseroinus Błocki; A(ii); abundance: occasional; trend: stable; speciesdata quality: medium; trend data quality: poor. • Pulsailla patens (L.) Mill.; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • G1.7 Thermophilous deciduous woodland; area: 40 ha; trend: decreasing; area data quality: medium; trend data quality: medium. Conservaion proposals. Create a state botanical reserve including the enire IPA. 177 Lysa Hora i Sinka Ukrainian name: Лиса гора і Стінка. Transliteraion/Translaion variants: Bald Hill and Clif. Area: 351 ha. Altitude: 288–427 m. Latitude: 49°47’00” N (49.7832°). Longitude: 24°44’21” E (24.7390°). Administrative regions. Lviv region: Zolochiv raion. Ownership: state. Biogeographic regions: coninental 178 V.A. Onyshchenko, T.D. Solomakha Habitats. Level 1. E – 36.8%; F – 1.0%; G – 60.5%; H – 1.7% Habitats. Level 2. E1 Dry grasslands – 36.2%; E5 Woodland fringes and clearings and tall forb stands – 0.3%; E7 Sparsely wooded grasslands – 0.3%; F3 Temperate and mediterraneanmontane scrub – 1.0%; G1 Broadleaved deciduous woodland – 44.5%; G3 Coniferous woodland – 12.0%; G4 Mixed deciduous and coniferous woodland – 1.5%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 2.5%; H3 Inland cliffs, rock pavements and outcrops – 1.7%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; E7.2 Sub-coninental parkland; F3.1 Temperate thickets and scrub; G1.6 Fagus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.F Highly artificial coniferous plantations; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H3.2 Basic and ultrabasic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: nature conservation and research – major, forestry – major. Protected areas: overlaps (196 ha) with state botanical nature monument “Lysa Hora i Hora Sypukha”, overlaps (about 345 ha) with Pivnichne Podillia naional nature park, included in Emerald Site “Pivnichne Podillia”. Threats: abandonment/reducion of land management – medium, burning of vegetaion – low. General description. Hills with beech forests, pine plantaions, grasslands and marl outcrops. The grasslands are dominated by Briza media, Carex lava, Carex humilis, Dactylis glomerata, Festuca pratensis, Festuca rubra, Festuca rupicola, Helictotrichon desertorum, Inula ensifolia, Teucrium chamaedrys. Frequent species are Allium lusitanicum s.l. (Allium montanum auct.), Anemone sylvestris, Asperula cynanchica, Bupleurum falcatum, Campanula sibirica, Centaurea pannonica, Euphorbia cyparissias, Galium verum, Lembotropis nigricans, Leontodon hispidus, Linum catharicum, Onobrychis arenaria, Pimpinella saxifraga, Plantago media, Potenilla incana (P. arenaria), Primula veris, Prunella grandilora, Ranunculus polyanthemos, Ranunculus zapalowiczii, Scabiosa ochroleuca, Thymus marschallianus, Thymus pannonicus, Salvia pratensis. Botanical significance. Important area for Carlina onopordifolia. Criterion A • Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł.; A(i), A(ii), A(iv); abundance: frequent (2000 individuals); trend: stable; species data quality: good; trend data quality: medium. Conservaion proposals: do not allow natural and ariicial aforestaion, expand state botanical monument “Lysa Hora i Hora Sypukha”. Literature 1. Дідух Я., Коротченко І. Ксеротермна рослинність північно-західного Поділля // Вісник Львівського ун-ту. Серія біологічна. – 2003. – 34. – С. 82–91. 2. Кагало О.О., Загульський М.М., Зеленчук А.Т., Сичак Н.М. Судинні рослини державного заказника “Лиса гора та гора Сипуха” в Золочівському районі Львівської області // Наукові основи збереження біотичної різноманітності: тематичний збірник Інституту екології Карпат НАН України. – Вип. 6. – Львів: Ліга-Прес, 2006. – С. 66–81. 3. Мельник В.І., Скоропляс І.О., Баточенко В.М. Сучасний стан популяцій Carlina onopordifolia (Asteraceae) на західному Волино-Поділлі // Укр. ботан. журн. – 2014. – 71, № 2. – С. 35–48. 4. Мельник В.И., Скоропляс И.О. Современное состояние популяций Сarlina onopordifolia Besser ex Szafer, Kulcz. & Pawl. в Украине // Austrian Journal of Technical and Natural Sciences. – 2014. № 9-10. – С. 21–24. 179 Lysohirka V.P. Kolomiychuk Ukrainian name: Лисогірка. Transliteraion/Translaion variants: Lysogirka. Area: 4.8 ha. Altitude: 32–43 m. Latitude: 47°39’44” N (47.6621°). Longitude: 35°06’19” E (35.1052°). Administrative regions. Zaporizhia region: Zaporizhia raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 65.0%; G – 30.0%; H – 5.0%. Habitats. Level 2. E1 Dry grasslands – 65.0%; G3 Coniferous woodland – 30.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 5.0%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); G3.F Highly artificial coniferous plantations; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: forestry – 100%. Protected areas: –. Threats: forestry (aforestaion) – high, burning of vegetaion – low. General description. Inland dunes on the right bank of the Dnipro river. Dry sand grasslands are dominated by Artemisia marschalliana, major co-dominant is Secale sylvestre. Species of signiicant constancy: Festuca beckeri, Koeleria sabuletorum, Dianthus platyodon, Oites borysthenica, Chondrilla juncea, Gypsophilla paniculata, Erigeron canadensis, Digitaria sanquinalis, Eragrosis minor, Kochia lanilora, Setaria pycnocoma, Tragus racemosus. Total 180 cover is 50–80%. Besides there are forest plantaions of Pinus pallasiana. Botanical significance. Single known locality of narrow endemic species Centaurea appendicata. Criterion A • Centaurea appendicata Klokov; A(iii); abundance: 270 individuals; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Create a state botanical nature monument. Literature 1. Коломійчук В.П. Сучасний список регіонально рідкісних судинних рослин Запорізької області // Промышленная ботаника. – 2011. – вып. 11. – С. 105‒111. 2. Мойсієнко І.І., Коломійчук В.П., Діденко В.І., Костіков І.Ю., Баданіна В.А., Захарова М.Я., Овсієнко В.М. Білоперлинні волошки берегів Каховського водосховища: сучасний стан популяцій та заходи з їх охорони // Чорноморськ. бот. журнал. – 2014. – Т. 10, № 3. – С. 352–357. 3. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Marina Hora V.A. Onyshchenko Ukrainian name: Мар’їна гора. Transliteraion/Translaion variants: Mar’yina Gora, Maria’s Hill. Area: 84.7 ha. Altitude: 57–114 m. Latitude: 48°55’42” N (48.9282°). Longitude: 38°09’16” E (38.1544°). Administrative regions. Donetsk region: Bakhmut (Artemivsk) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 96.1%; F – 0.2%; G – 1.5%; H – 2.2%. Habitats. Level 2. E1 Dry grasslands – 96.1%; F3 Temperate and mediterranean-montane scrub – 0.2%; G1 Broadleaved deciduous woodland – 1.5%; H2 Screes – 2.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%; H5.6 Trampled areas. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; nature conservaion and research – major; tourism/recreaion – minor. Protected areas: overlaps (about 80 ha) with regional botanical nature monument “Marina Hora”, overlaps (83 ha) with Emerald Site “Kreminski Lisy”). Threats: –. General description. Slope of the Siverskyi Donets valley with the steppe vegataion and chalk outcrops. Botanical significance. Important area for some endemic species of chalk outcrops. 181 Criterion A • Alyssum gymnopodum P.A.Smirn. (Odontarrhena gymnopoda (P.A.Smirn.) D.A.German); A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. • Diplotaxis cretacea Kotov; A(i); abundance: unknown: rare; trend: unknown; species data quality: por; trend data quality: poor. • Schivereckia podolica Andrz. ex DC. (Draba podolica (Besser) Rupr.); A(ii); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. • Syrenia talievi Klokov; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. calcareous spring mires – 45.0%; D5 Sedge and reedbeds, normally without free-standing water – 42.6%; F9 Riverine and fen scrubs – 0.3%. Futher habitat descripion. D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E3.4 Moist or wet eutrophic and mesotrophic grassland; F9.2 Salix carr and fen scrub. Land use: nature conservation and research – 100%. Protected areas: included in regional hydrological reserve “Luha-Svynoryika”, included in Emerald Site “Markovychi”. Threats: abandonment/reducion of land management – low, burning of vegetaion – low. General description. Major vegetaion type is the rich fens dominated by Schoenus ferrugineus, Cladium mariscus, Carex lava, Pragmites australis, Carex elata, Eriophorum laifolioum, with presence of Briza media, Calliergonella cuspidata, Carex panicea, Carex nigra, Drepanocladus intermedius, Drepanocladus polygamus, Lysimachia vulgaris, Molinia caerulea, Parnassia palustris, Potenilla erecta, Salix rozmarinifolia. Besides there are marshes dominated by Carex acuiformis, Carex elata, Phragmites australis without signiicant presence of calciphile species. Botanical significance. One of the largest rich fens in Ukraine. Literature 1. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Markovychi V.V. Datsiuk Ukrainian name: Марковичі. Area: 51.4 ha. Altitude: 198–205 m. Latitude: 50°43’48” N (50.7298°). Longitude: 24°43’13” E (24.7201°). Administrative regions. Volynska region: Lokachi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.1%; D – 87.6; E – 12.0%; %; F – 0.3%. Habitats. Level 2. E3 Seasonally wet and wet grasslands – 12.0%; D4 Base-rich fens and 182 Criterion C • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; area: 22 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Дацюк В.В., Андрієнко Т.Л Найбільший в Україні локалітет рідкісних угруповань Schoenus ferrugineus L. та Сladium mariscus (L.) Pohl (Cyperaceae) на Волинському лесовому плато ∕∕ Наук. вісник. Східноєвропейського національного університету імені Лесі Українки. Біологічні науки. – Луцьк. – 2013. – № 14. – С. 8–13. 183 Marmaroski Hory V.A. Onyshchenko, V.M. Virchenko Ukrainian name: Мармароські гори. Transliteraion/Translaion variants: Marmarosh Mountains, Maramureș Mountains. Area: 8464.0 ha. Altitude: 435–1940 m. Latitude: 47°56’41” N (47.9446°). Longitude: 24°18’14” E (24.3037°). Administrative regions. Zakarpatska region: Rakhiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.4%; D – 0.1%; E – 8.4%; F – 1.6%; G – 89.1%; H – 0.4%. Habitats. Level 2. C2 Surface running waters – 0.4%; E1 Dry grasslands – 0.6%; E4 Alpine and subalpine grasslands stands – 5.8%; E5 Woodland fringes and clearings and tall forb stands – 2.0%; F2 Arctic, alpine and subalpine scrub – 1.6%; G1 Broadleaved deciduous woodland – 7.0%; G3 Coniferous woodland – 14.2%; G4 Mixed deciduous and coniferous woodland – 67.9%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland (E1.71 Nardus stricta swards, E1.72 Agrosis – Festuca grassland); E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E4.1 Vegetated snow-patch; E4.2 Moss and lichen dominated mountain summits, ridges and exposed slopes; E4.3 Acid alpine and subalpine grassland; E4.4 Calcareous alpine and subalpine grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H2.4 Temperate-montane calcareous and ultra-basic screes; H3.1 Acid silicious inland clifs; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – minor, forestry – minor, nature conservation and research – major. Protected areas: included in Karpatskyi biosphere reserve (naional category), included in Carpathian biosphere reserve (UNESCO), included in Emerald Site “Carpathian Biosphere Reserve”, overlaps (8474.0 ha) with World Heritage Site “Primeval Beech Forests of the Carpathians and the Ancient Beech Forests of Germany” (core zone: 2243.6 ha, bufer zone: 6230.4 ha). Threats: climate change/sea level rise – low. General description. At lower alitudes, there prevails mixed forests co-dominated by Fagus sylvaica, Picea abies and Abies alba and pure Fagus sylvaica forests. The herb layer is composed predominantly of Anemone nemorosa, Athyrium ilix-femina, Dryopteris ilixmas, Galium odoratum, Mercurialis perennis, Oxalis acetosella, Symphytum cordatum. At higher alitudes, there are pure Picea abies forests and subalpine vegetaion. Subalpine vegetaion is represented mainly by Pinus mugo, Duschekia alnobetua (Alnus alnobetula), 184 Juniperus sibirica scrubs, Vaccinium myrillus heaths, grasslands dominated by Nardus stricta and Deschampsia cespitosa. Besides there are communiies dominated by Rhododendron myrifolium, Festuca inarmata, Festuca carpaica, Festuca saxailis, Poa deylii. Botanical significance. Important area for beech, mixed and spruce forests, subalpine habitats and species. Criterion A • Botrychium multifidum (S.G.Gmel.) Rupr.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Campanula abieina Griseb. & Schenk; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Campanula serrata (Kit.) Hendrych; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Dicranum viride (Sull. et Lesq.) Lindb.; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Hamatocaulis vernicosus (Mitt.) Hedenas (Drepanocladus vernicosus (Mitt.) Warnst.); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Narcissus angustifolius Curtis; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Poa graniica Braun.-Blanq. (Poa deylii Chrtek & V.Jira); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Tozzia carpathica Woł.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • C2.12 Hard water springs; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: poor. • D2.226 Peri-Danubian black-white-star sedge fens; area: 1 ha; trend: unknown; area data quality: poor; trend data quality: poor. 185 • E4.11 Boreo-alpine acidocline snow-patch grassland and herb habitats; area: 1 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.3 Acid alpine and subalpine grassland; area: 450 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.4 Calcareous alpine and subalpine grassland; area: 2 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.5 Subalpine moist or wet tall-herb and fern stands; area: 150 ha; trend: stable; area data quality: poor; trend data quality: poor. • F2.22 Alpide acidocline Rhododendron heaths; area: 3 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.12 Boreo-alpine riparian galleries; area: 80 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.A4 (*9180) Ravine and slope woodland; area: 30 ha; trend: stable; area data quality: poor; trend data quality: medium. • H2.3 Temperate-montane acid siliceous screes; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1.Біорізноманіття Карпатського біосферного заповідника / Кол. авт., Ред. рада: Я.І. Мовчан, Ф.Д. Гамор та ін. – К.: Інтерекоцентр, 1997. – 711 с. 2.Гамор Ф.Д., Волощук М.І., Антосяк Т.М., Козурак А.В. БЗ Карпатський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 45–72. 3.Гамор Ф.Д., Довганич Я.О., Покиньчереда В.Ф. та ін. Праліси Закарпаття. Інвентаризація та менеджмент. – Рахів, 2008. – 86 с. 4.Малиновський К.А. Рослинність високогір’я Українських Карпат. – К.: Наук. думка, 1980.– 280 с. 5.Малиновський К.А., Крічфалушій В.В. Рослинні угруповання високогір’я Українських Карпат. – Ужгород, 2002. – 244 с. woodland – 95.5%; G3 Coniferous woodland – 1.0%; H3 Inland clifs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0% Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.2 Low and medium alitude hay meadows; G1.6 Fagus woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus Medobory V.A. Onyshchenko Ukrainian name: Медобори. Area: 11811 ha. Altitude: 235–414 m. Latitude: 49°15’06” N (49.2515°). Longitude: 26°10’33” E (26.1758°). Administrative regions. Khmelnytskyi region: Chemerivtsi raion, Horodok raion; Ternopil region: Husiatyn raion, Pidvolochysk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.1%; D – 0.1%; E – 2.1%; F – 0.2%; G – 96.5%; H – 1.0%. Habitats. Level 2. C2 Surface running waters – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.1%; E1 Dry grasslands – 1.1%; E2 Mesic grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 0.2%; G1 Broadleaved deciduous 186 and related woodland; G3.F Highly artificial coniferous forestry plantations; H3.2 Basic and ultra-basic inland clifs; H3.5 Almost bare rock pavements, including limestone pavements; 187 H5.6 Trampled areas. Land use: agriculture (animals) – minor; forestry – minor, mowing/hay making – minor, nature conservation and research – 98%. Protected areas: overlaps with Medobory nature reserve (about 8786 ha), overlaps with Podilski Tovtry naional nature park (about 2810 ha), includes Satanivskyi state forest reserve (1015 ha), includes Ivakhnovenskyi state landscape reserve (1778 ha), includes Velyka and Mala Buhaikha state landscape reserve (66 ha), includes Vilkhovetski Tovtry regional botanical reserve (47 ha), overlaps with Emerald Site “Medobory Nature Reserve” (about 8786 ha), overlaps with Emerald Site “Podiliski Tovtry Naional Nature Park” (about 2950 ha). Threats: abandonment/reducion of land management – low. General description. A part of the Tovtry hills. Major vegetaion type is the broadleaved forest. The tree layer is formed mainly by Carpinus betulus, Quercus robur, Fraxinus excelsior. Main dominants of the herb layer are Aegopodium podagraria, Anemone nemorosa, Anemone ranunculoides, Carex pilosa, Corydalis cava, Isopyrum thalictroides, Lamium galeobdolon. Other typical species are Acer platanoides, Acer pseudoplatanus, Corydalis solida, Euonymus europaeus, Galium odoratum, Glechoma hirsuta, Milium efusum, Mercurialis perennis, Polygonatum hirtum, Polygonatum mulilorum, Pulmonaria obscura, Ranunculus cassubicus, Sambucus nigra, Stachys sylvaica, Stellaria holostea, Tilia cordata, Urica dioica. On the stony slopes and tops of the limestone hills, there occur forests dominated by Fraxinus excelsior and Acer platanoides with diferenial species Arum besseranum, Bromopsis benekenii, Hordelymus europaeus, Hylotelephium polonicum, Lamium maculatum, Lunaria rediviva, Melandrium dioicum, Scutellaria alissima, Viburum lantana. The area includes the easternmost natural Fagus sylvaica forest in the coninental biogeographical region. In some places there is the steppe vegetaion in complex with the shrub vegetaion. Main dominants of the steppes are Carex humilis, Festuca valesiaca s.l., Poa angusifolia. Prevailng species of shrubs are Chamaecyisus albus, Crataegus leiomonogyna, Juniperus communis, Prunus spinosa, Swida sanguinea (Cornus sanguinea). Hay medows in the loodplain of the Zbruch river are dominated by Arrhenatherum elaius, Dactylis glomerata, Poa pratensis. Besides in other places Calamagrosis epigeios meadows occur. Botanical significance. One of the best oak-hornbeam forests in the latland porion of Ukraine. Besides this area is important for Chamaecyisus podolicus and communiies of Juniperus communis. Other important species: Aconitum besseranum, Cypripedium calceolus, Chamaecyisus blockianus, Euphorbia volhynica, Schivereckia podolica (Draba podolica). Criterion A • Aconitum besserianum Andrz.; A(iiі); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. • Chamaecytisus podolicus (Błocki) Klásk. A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Schivereckia podolica (Besser) Andrz. ex DC. (Draba podolica (Besser) Rupr.); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion B • G1 Broadleaved deciduous woodland; area 11100 ha; % of indicator species: 13.0%; No of indicator species: 10; trend: increasing; species data quality: good; area data quality: good; trend data quality: good. Criterion C • F3.16 Juniperus communis scrub; area: 16 ha; trend: stable; area data quality: medium; trend data quality: poor. G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; area: 9000 ha; trend: increasing; area data quality: medium; trend data quality: good. • G1.A4 (*9180) Ravine and slope woodland; area: 200 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Onyshchenko V.A. Forests of order Fagetalia sylvaticae in Ukraine. – Kyiv: Alterpress, 2009. – 212 p. 2. Szafer W. Geobotaniczne stosunki Miodoborόw Galicyjskich // Rozpr. Wydz. Matemat.-Przyrod. Akad. Umiejętności. – 1910. – Ser. 3, Dz. B, T. 10. – S. 63–172. 3. Данилків І.С., Рабик І.В. Мохоподібні (Bryophytes) природного заповідника “Медобори” // Чорноморський ботан. журн. – 2007. – 3, № 1. – С. 85–99. 4. Коломієць І.В., Дудка І.О., Тихоненко Ю.Я. Іржасті гриби заповідника “Медобори” // Укр. ботан. журн. – 1996. – 53, № 3. – С. 201–207. 5. Кондратюк С.Я. Лишайники заповідника “Медобори” // Укр. ботан. журн. – 1995. – 52, № 1. – С. 141–144. 6. Кондратюк С.Я., Коломієць І.В. Нові для України види лишайників та ліхенофільних грибів заповідника “Медобори” // Укр. ботан. журн. – 1997. – 54, № 1. – С. 42–47. 7. Котов М. Геоботанический очерк буковых лесов по р. Збруч // Журнал Русского ботанического общества. – 1930. – 15, № 1–2. – P. 139–148. 8. Мельник В.І., Корінько О.М. Букові ліси Подільської височини. – Київ: Фітосоціоцентр, 2005. – 152 с. 9. Оліяр Г.І. Рослини Червоної книги України в природному заповіднику “Медобори”// Заповідна справа в Україні. – 1995. – Т. 1. – С. 11–12. 10. Оліяр Г.І. Конспект флори природного заповідника “Медобори” // Наукові записки ТДПУ. Серія: Біологія, № 2 (17). – 2002. – С. 18–25. 11. Оліяр Г.І. Зміни у флорі природного заповідника “Медобори” за минуле сторіччя // Роль природно-заповідних територій Західного Поділля та Юри Ойцовської у збереженні біолог. та ландшафтн. різноманіття, – Гримайлів, 2003. – С. 333–338. 12. Оліяр Г. І. Фітораритети природного заповідника “Медобори” з філією “Кременецькі гори” в міжнародних червоних списках // Природно-заповідний фонд України – минуле, сьогодення, майбутнє. Матеріали міжнародної науковопрактичної конференції, присвяченої 20-річчю природного заповідника “Медобори” (смт. Гримайлів, 26–28 травня 2010 р.) – Тернопіль: Підручники і посібники, 2010. – С. 460–464. 13. Онищенко В.А. Рослинність карбонатних відслонень природного заповідника “Медобори” // Укр. фітоцен. зб. – Сер. A. – 2001. – 1 (17). – С. 86–104. 14. Онищенко В.А., Оліяр Г.І. // Рідкісні лісові угруповання природного заповідника “Медобори” // Укр. ботан. журн. – 1998. – 55, № 4. – С. 413–416. 15. Онищенко В.А., Оліяр Г.І. ПЗ Медобори // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 254–276. 16. Смеречинская Т. А. Закономерности распространения лишайников по фитоценозам природного заповедника “Медоборы” // Заповідна справа в Україні. – 2005. – Т.11, Випуск 1. – С. 9–15. 188 189 • Medvezhanka V.A. Onyshchenko, M.M. Peregrym Ukrainian name: Медвежанка. Area: 7849.0 ha. Altitude: 80–223 m. Latitude: 48°13’24” N (48.2234°). Longitude: 39°31’34” E (39.5260°). Administrative regions. Luhansk region: Dovzhansk (Sverdlovsk) raion, Lutuhyne raion, Sorokyne (Krasnodon) raion. Ownership: state. Biogeographic regions: steppic ultra-basic inland cliffs; H5.6 Trampled areas; I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – major; agriculture (arable) – minor; extracion (minerals) – minor; forestry – minor; nature conservaion and research – minor. Protected areas: overlaps (about 1135 ha) with regional landscape reserve “Krasnianske Vodoskhovyshche”, overlaps (7790 ha) with Emerald Site “Vedmezhanka”. Threats: agricultural intensification/expansion (arable) – medium, agricultural intensiicaion/expansion (grazing) – low, extracion (minerals/quarries) – low, forestry (aforestaion) – low. General description. The area is situated within the Donetsk Ridge. Dominants of the steppe vegetaion are Festuca valesiaca, Bothriochloa ischaemum, Bromopsis riparia, Bromopsis inermis, Elytrigia intermedia, Poa angusifolia, Sipa capillata, S. lessingiana, S. irsa, S. ucrainica. On the neutral outcrops of slate and sandstone, there are Thymus marschallianus, Pimpinella titanophila, Artemisia marschalliana, Agropyron pectinatum. Botanical signiicance. One of the largest areas of the steppe vegetaion in Ukraine. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 7000 ha; trend: decreasing; area data quality: good; trend data quality: poor. Conservaion proposals. Do not allow plowing. Сreate a naional nature park. Literature 1. Природно-заповідний фонд Луганської області // О.А. Арапов (заг. ред.), Т.B. Сова, О.А. Cавенко, В.Б. Фєрєнц, Н.У. Кравець, Л.Л. Зятьков, Л.О. Морозова. Довідник. – 3-е вид., доп. і переробл. – Луганськ: “Луганська правда”, 2013. – 224 с. Mehanom Habitats. Level 1. E – 90.0%; F – 1.0%; G – 3.0%; H – 1.0%; I – 5.0%; Habitats. Level 2. E1 Dry grasslands – 89.9%; E2 Mesic grasslands – 0.1%; F3 Temperate and mediterranean-montane scrub – 1.0%; G1 Broadleaved deciduous woodland – 2.6%; G3 Coniferous woodland – 0.4%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.8%; I1 Arable land and market gardens – 5.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G3.F Highly artificial coniferous plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and V.A. Onyshchenko Ukrainian name: Меганом. Transliteraion/Translaion variants: Meganom. Area: 1936.0 ha. Altitude: 0–358 m. Latitude: 44°48’55” N (44.8152°). Longitude: 35°05’34” E (35.0929°). Administrative regions. Autonomous Republic of Crimea: Sudak city; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 6.6%; B – 1.3%; E – 63.1%; F – 4.7%; G – 20.7%; H – 3.7%; J – 0.1%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.2%; A2 Littoral sediment – 0.2%; A3 Infralittoral rock and other hard substrata – 2.1%; A5 Sublittoral sediment – 4.1%; B2 Coastal shingle – 0.1%; B3 Rock cliffs, ledges and shores, including the supralittoral – 1.2%; E1 Dry grasslands – 59.9%; E6 Salt steppes – 3.1%; F3 Temperate and mediterraneanmontane scrub – 2.7%; F7 Spiny Mediterranean heaths – 2.0%; F9 Riverine and fen scrubs – 0.0%; G1 Broadleaved deciduous woodland – 20.7%; H2 Screes – 0.5%; H3 Inland clifs, rock pavements and outcrops – 3.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. 190 191 Futher habitat description. A2.1 Litoral coarse sediment; A2.5 Coastal saltmarshes and saline reedbeds; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.5 Sublitoral macrophyte-dominated sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E1.3 Mediterranean xeric grassland; F3.2 Submediterranean deciduous thickets and brushes; F7.4 Hedgehog-heaths; F9.3 Southern riparian galleries and thickets; G1.7 Thermophilous deciduous woodland; G1.C Highly ariicial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultrabasic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: tourism/recreaion – minor, urban/industrial/transport – 2% (wind turbines, road). Protected areas: includes Pivostriv Mehanom regional complex nature monument (651.6 ha), included in Emerald Site “Mehanom”. Threats: development (recreaion/tourism) – low, eutrophicaion – low. General description. Mehanom is a peninsula in the southeastern part of Crimea. This is the most arid place in Crimea. Hills are covered chiely with the steppe vegetaion. Maximum alitude is 358 m. Slope to the sea is steep, with clifs about 100 m high. Adjacent sea is included. Surface of the shore consists of rocks, boulders, pebble and gravel. Dominants of the steppe vegetaion are Agropyron pecinatum, Bothriochloa ischaemum, Bromopsis cappadocica, Festuca valesiaca, Koeleria cristata, Sipa capillata, Sipa ponica, Sipa ucrainica. Typical are Achillea nobilis, Achillea millefolium, Galatella linosyris, G. villosa, Cruciata taurica, Inula germanica, Inula oculus-christi, Jurinea roegneri, Centaurea salonitana, Limonium platyphyllum, Linum austriacum, Linum nervosum, Limonium squamulosum, Nepeta ucranica, Onosma taurica, Onosma visianii, Phlomis pungens, Poterium polygamum, Psephellus trinervius, Salvia nemorosa s.l., Scabiosa argentea, Stachys cretica subsp. velata. Petrophyic steppe difers with presence of Alyssum tortuosum (Odontarrhena tortuosa), Ephedra distachya, Euphorbia petrophila, Fumana procumbens, Paronychia cephalotes, Siederitis syriaca, Thymus roegneri, Thymus tauricus. Salt steppes are dominanted by Artemisia taurica, Artemisia lercheana, Camphorosma monspeliaca, Petrosimonia brachiata. Dry grasslands of mediterranean type with signiicant paricipaion of annual species (Aegilops biuncialis, Aegilops cylindrica, Aegilops triuncialis, Alyssum hirsutum, Alyssum desertorum, Bromus japonicus, Bromus hordeaceus, Bromus sguarrosus, Gaudinopsis macra, Taeniatherum asperum, Taeniatherum crinitum) occupy about 100 ha. In dry rocky habitats, there is open vegetaion with Alyssum murale, Asphodeline taurica, Cleistogenes serotina, Ephedra distachya, Euphorbia petrophila, Fumana procumbens, Hedysarum candidum, Helianthemum grandiflorum, Helianthemum nummularium, Medicago cretacea, Melica monticola, Melica taurica, Pimpinella tragium, Poa sterilis, Sideritis syriaca subsp. catillaris, Sedum acre, Sedum hispanicum, Seseli gummiferum, Teucrium polium, Thymus roegneri, Thymus tauricus, Veronica multifida. On the sea beach, there occur Crambe mariima, Cynanchum acutum, Limonium gmelini, Peganum harmala, several species of Atriplex and Soda. Main species of trees in sparse woods is Quercus pubescens. Besides there are Carpinus orientalis, Clematis vitalba, Cotoneaster tauricus, Cotinus coggygria, species of Crataegus, Paliurus spina-christi, Pyrus communis, Pyrus eleagnifolia. The herb layer consists mainly of steppe and petrophyic species, some wood species occur too. Shrub communiies are dominated by Rosa canina, R. spinosissima, Paliurus spina-christi, Cotinus coggygria. In valleys, there are small areas of Tamarix ramosissima, Tamarix tetrandra and Eleagnus angusifolia stands. In the sea at depths to 3 m, dominant species are Ceramium ciliatum, Cladostephus vericillatus, Corallina mediterranea, Cystosera barbata, Cystoseira crinita, Dilophus fasciola, Enteromorpha compressa, Grateloupia dichotoma, Polysiphonia opaca. At depths 3–10 m, there predominate Chondria tenuissima, Cladophora albida, Cladophora dalmaica, Cystoseira crinita, Сystoseira barbata, Phyllophora nervosa, Ulva rigida, Zostera marina, Zostera nolii (Nanozostera nolii). Protected areas: –. Botanical significance. Important area for conservaion of dry grasslands, sea and inland clifs, marine macrophytes. There are threatened endemic species Astragalus reduncus, Astragalus setosulus, Onobrychis pallasii, Onosma polyphylla, Stipa syreistschikowii. Criterion A • Astracantha arnacantha (M.Bieb.) Podlech; A(iv); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Astragalus reduncus Pall.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Astragalus setosulus Gontsch.; A(i), A(ii), A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Onobrychis pallasii (Willd.) M.Bieb.; A(iii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Onosma polyphylla Ledeb.; A(ii), A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Stipa syreistschikowii P.Smirn.; A(ii), A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. 192 193 Criterion C • A3 Infralittoral rock and other hard substrata; area: 80 ha; trend: stable; area data quality: medium; trend data quality: poor. • A5 Sublitoral sediment; area: 80 ha; trend: stable; area data quality: medium; trend data quality: medium. • B3.3 Rock cliffs, ledges and shores, with angiosperms; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: medium. • E1.2 Perennial calcareous grassland and basic steppes; area: 700 ha; trend: stable; area data quality: medium; trend data quality: medium . • F7 Spiny Mediterranean heaths; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. • F9.3 Southern riparian galleries and thickets; area: 1 ha; trend: unknown; area data quality: poor; trend data quality: poor. Literature 1. Костенко Н.С., Дикий Е.А., Заклецкий А.А., Марченко В.С. Аквальні комплекси бухти Лісьей та півострова Меганом – перспективі об'єкти природнозаповідного фонду // Современные проблемы экологии Азово-Черноморского региона: материалы II международной конференции (Керчь, 26–27 июня 2006 г.). – Керчь: ЮгНИИРО, 2006. – С. 103–108 2. Костенко Н.С., Дикий Е.А., Заклецкий А.А., Марченко В.С. Донная растительность приоритетных акваторий юго-восточного Крыма: современное состояние и необходимые меры по сохранению // Заповедники Крыма – 2007. Материалы IV международной научно-практической конференции, посвященной 10-летию проведения международного семинара "Оценка потребностей сохранения биоразнообразия Крыма" (Гурзуф, 1997). Часть 1. Ботаника. Общие вопросы охраны природы. – Симферополь, 2007. – С. 63–68. 3. Миронова Л.П., Шатко В.Г. Полуостров Меганом в юго-восточном Крыму (природные условия, флора, растительность // Геополитика и экогеодинамика регионов. – 2013. – Т. 9, Вып. 2, Ч. 2. – С. 26–64. Trampled areas. Land use: forestry – major, nature conservation and research – minor. Protected areas: overlaps with regional forest reserve “Mishkovo-Pohorilove”. Threats: forestry (aforestaion) – medium, development (urbanization) – low. General description. Terrace of the Inhul river with Pinus pallasiana and Pinus sylvestris plantaions and sand grasslands. Sand grasslands are dominated by Carex colchica, Artemisia marschalliana, Festuca beckeri, Koeleria sabuletorum, Thymus pallasianus. Other frequent species are Sipa borysthenica, Scabiosa ucrainica, Achillea ochroleuca, Helichrysum corymbiforme, Astragalus varius, Anchusa gmelinii, Jurinea charcoviensis, Tragopogon borysthenicus, Alyssum savranicum (Odontarrhena savranica), Secale sylvestre. Density of Centaurea margaritacea in natural grasslands is 3 to 30 individuals per 100 m2. Botanical significance. 100% of global populaion of narrow endemic species Centaurea margaritacea s. str. Criterion A • Centaurea margaritacea Ten. s. str.; A(iii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Create a state botanical reserve instead of local forest reserve “Mishkovo-Pohorilove”. Restore sand grasslands. Mishkovo-Pohorilove O.M.Derkach, H.V. Kolomiets Ukrainian name: Мішково-Погорілове. Area: 152 ha. Altitude: 2–41 m. Latitude: 47°00’54” N (47.0148°). Longitude: 32°06’11” E (32.1029°). Administrative regions. Mykolaiv region: Vitovka (Zhovtnevyi) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 8.0%; G – 90.0%; H – 2.0%. Habitats. Level 2. E1 Dry grasslands – 8.0%; G3 Coniferous woodland – 90.0%; H5 Miscellaneous inland habitats with very sparse or no vegetaion – 2.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); G3.F Highly artificial coniferous plantations; H5.6 194 Literature 1.Деркач О.М. Ключові ботанічні території Миколаївщини: сучасний стан та проблеми збереження // Теорія і практика заповідної справи в Україні. Зб.наук.праць. – К., 2005. – С.167–173. 2.Деркач О.М. Нижньоінгульське // Південно-Бузький меридіональний екологічний коридор: стислий огляд біорізноманіття та найцінніші території / Під ред. В. Костюшина. – К., 2007. – С. 53. 195 3.Коломієць Г.В. Перлинні волошки секції Pseudophalolepis Klok. ряду Margaritacea Klok. Питання систематики та охорони // Укр. фітоценологічний зб. – Вип. 1–2 (12–13). – К.: Фітосоціоцентр, 1999. – С. 165–169. 4.Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. (Centaurea L.) // Укр. ботан. журн. – 1991. – 48, № 3. – С. 78–80. 5.Крицька Л.І., Деркач О.М. Волошка первинноперлинна Centaurea margaritacea Ten. / Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 304. 6.Перлини піщаної флори у пониззях Південного Бугу та Інгулу. Cерія: Збереження біорізноманіття в Приморсько-степовому екокоридорі / Під ред. Г.В. Коломієць. – К.: Громадська організація “Веселий Дельфін”, 2008. – 60 c. presence of psammophyic species Artemisia marschalliana, Sipa borysthenica, Ephedra distachya, Helicrysum arenarium. A large area is occupied by salt meadows (dominats: Molochnyi Lyman V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Молочний лиман. Area: 28196.0 ha. Altitude: 0–20 m. Latitude: 46°34’42” N (46.5782°). Longitude: 35°19’44” E (35.3289°). Administrative regions. Zaporizhia region: Melitopol raion, Pryazovsk raion, Yakymivka raion . Ownership: state. Biogeographic regions: steppic Habitats. Level 1. A – 85.2%; C – 0.7%; D – 1.1%; E – 12.9%; H – 0.1%. Habitats. Level 2. A2 Littoral sediment – 17.0%; A5 Sublittoral sediment – 68.2%; C1 Surface standing waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.6%; D5 Sedge and reedbeds, normally without free-standing water – 0.2%; D6 Inland saline and brackish marshes and reedbeds – 0.9%; E1 Dry grasslands – 1.0%; E6 Salt steppes – 11.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.3 Littoral mud; A2.5 Coastal saltmarshes and saline reedbeds; A5.3 Subittoral mud; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; D6.1 Inland saltmarshes; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E1.2 Perennial calcareous grassland and basic steppes; E6.2 Continental inland salt steppes; H5.6 Trampled areas. Land use: agriculture (animals) – minor; nature conservaion and research – major. Protected areas: overlaps (about 22730 ha) with Pryazovskyi naional nature park, overlaps (about 22400 ha) with Ramsar Site “Molochnyi Liman”, overlaps (about 22730 ha) with Emerald Site “Pryazovskyi Naional Nature Park”. Threats: –. General description. A lagoon in the northwestern part of the Sea of Azov and the mouth of the Molochna river in the nothern part of the lagoon. Connecion with the sea is intermitent. Level of water is unstable. A large area of the botom is exposed in the dry season. The right bank is rather high. There is the steppe vegetaion dominated by Agropyron pecinatum, Festuca valesiaca, Koeleria cristata, Sipa lessingiana, S. pulcherrima, S. ucrainica with 196 Elytrigia elongata, Puccinellia distans, Aeluropus litoralis, Juncus gerardii) and wet halophyic communiies (dominants: Phragmites australis, Scirpus tabernaemontani, Juncus maritimus, Bolboschoenus maritimus). In the most saline habitats, there dominate Halocnemum strobilaceum, Salicornia perennans, Suaeda prostrata, Halimione pedunculata, H. verrucifera, Limonium caspium, L. meyeri. On elevated areas of the let bank there are salt 197 steppes with dominance of Festuca valesiaca s.l., Camphorosma monspeliaca, Agropyron pecinatum, Koeleria cristata, Crinitaria villosa. On the southern side of the bar, there are litoral communiies with Argusia sibirica, Cakile euxina, Leymus sabulosus, Salsola pontica. In some places, there are aquaic communiies of Zostera marina, Zannichellia major, Myriophyllum spicatum, Ceratophyllum demersum, Potamogeton pecinatum (Stuckenia pecinata). Botanical significance. Important area for halophyic vegetaion, Zostera marina and some threatened steppe species. Criterion A • Allium pervesitum Klokov.; A(i), A(iv); abundance: rare; trend: stable; species data quality: good; trend data quality: good. • Allium regelianum A.Becker ex Iljin.; A(ii); abundance: rare (100–150 individuals); trend: unknown; species data quality: good; trend data quality: poor. • Ferula orientalis L.; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Zostera marina L.; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • A2.5 Coastal saltmarshes and saline reedbeds; area: 500 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E6.2 Coninental inland salt steppes; area: 3300 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Дубина Д.В., Шеляг-Сосонко Ю.Р. Тенденції антропогенних змін плавневоліторальних фітосистем р. Молочної // Укр. ботан. журн. – 1996. – 53, № 1–2. – С. 31–37. 2. Дубовий М.С., Дмитренко Є.М., Коломійчук В.П. Флора і рослинність Молочного лиману // Зб. доп. VІ Міжнар. науков. конф. аспірантів і студентів “Охорона навколишнього середовища та раціональне використання природних ресурсів” (17–19 квітня 2007 р., м. Донецьк). – Т. 1. – Донецьк: ДонНТУ, ДонНУ, 2007. – С. 176–177. 3. Коломийчук В.П., Подорожный С.Н. Флора берегов Молочного лимана // Біологічний вісник Мелітопольського держ. пед. університуту ім. Богдана Хмельницького. – 2013. – № 2. – С. 128–135. 4. Коломійчук В.П., Тищенко О.В. НПП Приазовський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 410–428. 5. Коломійчук В.П., Яровий С.О. Конспект флори судинних рослин Приазовського національного природного парку. – К.: Альтерпрес, 2011. – 296 с. 6. Тищенко О.В. Рослинність приморських кіс північного узбережжя Азовського моря. – Київ: Фітосоціоцентр, 2006. – 156 с. Latitude: 51°37’43” N (51.6285°). Longitude: 26°17’05” E (26.2846°). Administrative regions. Rivne region: Zarichne raion, Volodymyrets raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.02%; D – 10%; F – 0.1%; G – 90%. Habitats. Level 2. C1 Surface standing waters – 0.01%; C2 Surface running waters – 0.02%; D1 Raised and blanket bogs – 1%; D2 Valley mires, poor fens and transition mires – 8%; D5 Sedge and reedbeds, normally without free-standing water – 1%; F9 Riverine and fen scrubs – 0.1%; G1 Broadleaved deciduous woodland – 15%; G3 Coniferous woodland – 25%; G4 Mixed deciduous and coniferous woodland – 50%. Morochno-2 Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D1.1 Raised bogs; D2.3 Transiion mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.5 Broadleaved swamp V.A. Onyshchenko Ukrainian name: Морочно-2. Area: 4487 ha. Altitude: 148–159 m. 198 199 woodland not on acid peat; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.1 Mixed swamp woodland. Land use: forestry – minor, nature conservation and research – 100%. Protected areas: includes Khynotskyi state botanical reserve (2267 ha), includes Svarytsevytskyi state botanical reserve (2220 ha), included in Emerald Site “Dubrovytskyi”. Threats: –. General description. Wooded raised bogs and transiional mires with smaller areas of mires without the tree layer. Dominants: Pinus sylvestris, Betula pubescens, Carex lasiocarpa, Eriophorym vaginatum, Ledum palustre, Vaccinium oxycoccos (Oxycoccus palustris), Phragmites australis, Sphagnum cuspidatum, Sphagnum fallax, Sphagnum magellanicum, Sphagnum fuscum. Botanical significance. The largest area of wooded oligotrophic and mesotrophic mires with Pinus sylvestris and Betula pubescens in Ukraine. Criterion C • G1.51 Sphagnum Betula woods; area: 600 ha; trend: stable; area data quality: poor; trend data quality: poor. • G3.E Nemoral bog conifer woodland; area: 1000 ha; trend: stable; area data quality: poor; trend data quality: poor. • X04 Raised bog complexes; area: 40 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Land use: agriculture (animals) – minor; nature conservaion and research – major. Protected areas: includes Mykhailivskyi Step regional landscape reserve (1343.1 ha), included in Emerald Site "Mykhailivskyi Steppe". Threats: –. General description. Grasslands dominated by Festuca valesiaca, Sipa capillata, S, lessingiana, S. pulcherrima, S. ucrainica, Caragana frutex, Amygdalus nana, Koeleria cristata, Poa angusifolia. On stony calcareous soil, there prevail Sipa asperella, Thymus Mykhailivskyi Step V.A. Onyshchenko, O.M. Derkach Ukrainian name: Михайлівський степ. Transliteraion/Translaion variants: Myhaylivskyi Steppe. Area: 1774.0 ha. Altitude: 12–89 m. Latitude: 47°24'51" N (47.4140°). Longitude: 31°37'43" E (31.6284°). Administrative regions. Mykolaiv region: Voznesensk raion, Nova Odesa raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 95.9%; F – 0.3%; G – 3.3%; H – 0.5%. Habitats. Level 2. E1 Dry grasslands – 95.0%; E2 Mesic grasslands – 0.9%; F3 Temperate and mediterranean-montane scrub – 0.3%; G1 Broadleaved deciduous woodland – 3.3%; H2 Screes – 0.2%; H3 Inland cliffs, rock pavements and outcrops – 0.2%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.C Highly ariicial broadleaved deciduous forestry plantaions; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. 200 dimorphus, Koeleria brevis, Jurinea brachycephala with Allium lavescens, Astragalus albidus, A. ucrainicus, A. corniculatus, Centaurea marschalliana, Dianthus pseudoarmeria, Genista scythica, Gypsophila collina, Hedysarum grandilorum, Linaria macroura, Linum linearifolium, Pimpinella itanophila, Teucrium polium. Botanical significance. One of the best steppe areas west to the Dnipro river. Criterion A • Chamaecyisus graniicus (Rehmann.) Rothm.; A(iii); abundance: occasional; trend: stable; species data quality: poor; trend data quality: poor. • Crambe tataria Sebeok.; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. 201 • Gymnospermium odessanum (DC.) Takht.; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. • Tulipa hypanica Klokov et Zoz; A(iii); abundance: occasional; trend: stable; species data quality: poor; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1700 ha; trend: stable; area data quality: good; trend data quality: good. Conservaion proposals. Include in Yelanetskyi nature reserve. Literature 1. Південно-Бузький меридіональний екологічний коридор: стислий огляд біорізноманіття та найцінніші території / під ред. В. Костюшина. – К., 2007. – 92 с. Literature 1.Деркач О.М. Ключові ботанічні території Миколаївщини: сучасний стан та проблеми збереження // Теорія і практика заповідної справи в Україні. Зб.наук.праць. – К., 2005. – С.167–173. 2.Коломієць Г.В. Перлинні волошки секції Pseudophalolepis Klok. ряду Margaritacea Klok. Питання систематики та охорони // Укр. фітоценологічний зб. – Вип. 1–2 (12–13). – К.: Фітосоціоцентр, 1999. – С. 165–169. Mykhailo-Laryne O.M.Derkach, H.V. Kolomiets Ukrainian name: Михайло-Ларине. Area: 39.6 ha. Altitude: 10–45 m. Latitude: 47°08'14" N (47.1373°). Longitude: 32°13'00" E (32.2165°). Administrative regions. Mykolaiv region: Vitovka (Zhovtnevyi) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 30.0%; G – 69.0%; H – 1.0%. Habitats. Level 2. E1 Dry grasslands – 30.0%; G3 Coniferous woodland – 69.0%; H5 Miscellaneous inland habitats with very sparse or no vegetaion – 1.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); G3.F Highly artificial coniferous plantations; H5.6 Trampled areas. Land use: forestry – major. Protected areas: includes local botanical reserve "Mykhailo-Larynskyi" (14.8 ha) Threats: forestry (aforestaion) – medium. General description. A part of sand terrace above the loodplain of the Inhul river. Forest plantaions of Pinus pallasiana and Pinus sylvestris in comlex with dry sand grasslands. Dominant species of the grasslands are Carex colchica, Artemisia marschalliana. Other typical species are Anchusa gmelinii, Centaurea adpressa, Centaurea margarita-alba, Dianthus membranaceus, Euphorbia seguieriana, Gypsophila paniculata, Helichrysum arenarium, Linaria genisifolia, Scabiosa ucrainica, Sipa borysthenica, Thymus pallasianus. Botanical significance. 40% of global populaion of narrow endemic species Centaurea margarita-alba s. str. Criterion A • Centaurea margarita-alba Klokov; A(iii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Remove trees. Create a state botanical reserve instead of local botanical reserve "Mykhailo-Larynskyi" including the enire IPA. Restore sand grasslands in adjacent area. 202 3. Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. (Centaurea L.) // Укр. ботан. журн. – 1991. – Т. 48, № 3. – С. 78–80. 4. Крицька Л.І., Деркач О.М., Собко В.Г. Волошка білоперлинна Centaurea margaritaalba Klokov / Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 305. 5.Перлини піщаної флори у пониззях Південного Бугу та Інгулу. Cерія: Збереження біорізноманіття в Приморсько-степовому екокоридорі / Під ред. Г.В. Коломієць. – К.: Громадська організація "Веселий Дельфін", 2008. – 60 c. Mys Marian Ukrainian name: Мис Март'ян. Transliteraion/Translaion variants: Cape Marian, Cape Martyan. Area: 128.0 ha. Altitude: 0–240 m. 203 V.A. Onyshchenko Latitude: 44°30'40" N (44.5110°). Longitude: 34°14'56" E (34.2487°). Administrative regions. Autonom. Republic of Crimea: Yalta city; Territ. waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 7.0%; B – 1.0%; E – 0.1%; G – 91.4%; H – 0.5%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.1%; A2 Littoral sediment – 0.9%; A3 Infralittoral rock and other hard substrata – 3.0%; A5 Sublittoral sediment – 3.0%; B2 Coastal shingle – 0.8%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.2%; E1 Dry grasslands – 0.1%; G1 Broadleaved deciduous woodland – 33.2%; G3 Coniferous woodland – 35.0%; G4 Mixed deciduous and coniferous woodland – 23.2%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 0.2%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. A2.1 Litoral coarse sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.3 Mediterranean xeric grassland; G1.7 Thermophilous deciduous woodland; G3.5 Pinus nigra woodland; G3.9 Coniferous woodland dominated by Cupressaceae or Taxaceae; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: nature conservaion and research – 98%; tourism/recreaion – minor. Protected areas: overlaps (about 126 ha) with Mys Marian nature reserve, overlaps (94 ha) with Emerald Site "Mys Marian". Threats: burning of vegetaion – medium, development (recreaion/tourism) – low. General description. The IPA is situated in the southern part of the Crimea. It includes a slope near the sea with woods at alitudes up to 240 m and 50 m wide strip of the sea. The largest area is occupied by broadleaved woods dominated by Quercus pubescens with admixture of Arbutus andrachne, Fraxinus angusifolia, Juniperus excelsa, Pinus pallasiana. The shrub layer is dominated by Carpinus orientalis, Cornus mas, Juniperus oxycedrus, the lower shrub sublayer consists of Ruscus ponicus. In the herb layer, there are Achnatherum bromoides, Aegonychon purpureocaeruleum, Brachypodium rupestre, Carex cuspidata, Carex hallerana, Elytrigia nodosa, Festuca valesiaca. Juniperus excelsa woods also occupy a large area. Their shrub layer is composed of Juniperus oxycedrus (predominantly), Bupleurum fruicosum, Carpinus orientalis, Cornus mas, Paliurus spina-chrisi and lower shrubs such as Cistus tauricus, Hippocrepis emeroides, Jasminum fruicans, Ruscus ponicus. In the herb layer, there prevail Achnatherum bromoides, Carex cuspidata, Carex hallerana, Elytrigia nodosa, Fumana procumbens, Helianthemum canum, Helianthemum stevenii, Teucrium chamaedrys, Teucrium polium, Thymus roegneri. Smaller area is covered by Pinus pallasiana forest with dominance of Asperula stevenii, Brachypodium rupestre, Carex hallerana, Dorycnium herbaceum, Galium mollugo, Laser trilobum, Teucrium chamaedrys. Substrate types of the beach are unmobile rock and shingle. In the sea, there dominate Cystoseira crinita, Cystoseira barbata, Zostera marina, Zostera nolii (Nanozostera nolii). Considerable areas are occupied by screes and outcrops. Litoral habitats are represented by shingle beach and rocks. Botanical significance. Important for conservaion of Quercus pubescens woods, Juniperus excelsa woods, Brassica taurica. Criterion A • Brassica taurica (Tzvelev) Tzvelev (Brassica sylvestris Mill. subsp. taurica Tzvel.); A(i), A(ii); abundance: 30 individuals; trend: luctuaing; species data quality: good; trend data quality: good. • Ophrys oestrifera M.Bieb.; A(ii); abundance: 70 individuals; trend: stable; species data quality: good; trend data quality: medium. Criterion B • G1 Broadleaved deciduous woodland; area 75 ha; % of indicator species: 19.5%; No of indicator species: 15; trend: increasing; species data quality: good; area data quality: good; trend data quality: medium. Criterion C • G3.5 Pinus pallasiana and Pinus banaica forests; area: 5 ha; trend: stable; area data quality: medium; trend data quality: medium. • G3.9 Coniferous woodland dominated by Cupressaceae or Taxaceae; area: 40 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Белич Т.В. К изучению бриофлоры заповедника "Мыс Мартьян" // Заповедники Крыма. Заповедное дело, биоразнообразие, экообразование: Матер. III научн. конф. (22 апреля 2005 г., Симферополь, Крым). – Ч. I. – Симферополь, 2005. – С. 141–144. 2. Голубева И.В., Крайнюк Е.С. Аннотированный каталог высших растений заповедника "Мыс Мартьян". – Ялта, ГНБС. – 1987. – 40 с. 3. Шеляг-Сосонко Ю.Р., Дидух Я.П., Молчанов Е.Ф. Государственный заповедник "Мыс Мартьян". – Киев: Наук. думка, 1985. – 260 с. 4. Григоров А.Н. Естественное возобновление и возрастная структура насаждений можжевельника высокого в заповеднике "Мыс Мартьян" // Труды Никит. ботан. сада. – 1982. – Т. 86. – С. 35–44. 5. Ена А.В. Современное состояние крымских популяций земляничника мелкоплодного // Природоохранные аспекты изучения Горного Крыма. – Симферополь, 204 205 1986. – С. 26–30. 6. Крайнюк Е.С. Редкие виды высших растений в заповеднике "Мыс Мартьян" // Бюл. Никит. ботан. сада. – 1988. – Вып. 67. – С. 20–25. 7. Крайнюк Е.С. Современное состояние раритетного фитофонда заповедника "Мыс Мартьян" // Труды Никит. ботан. сада. – 2001. – Т. 120. – С. 63–73. 8. Крайнюк Е.С. Растения Красной книги Украины в природном заповеднике "Мыс Мартьян" // рослинний світ у Червоній книзі України: впровадження Глобальной стратегії збереження рослин. Матеріали міжнар. конф. (11 – 15 жовтня 2010 р.), Київ. – Київ: Альтерпрес, 2010. – С. 274–277. 9. Крайнюк К.С., Маслов І.І. ПЗ Мис Мартьян // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 277–290. 10. Куликов Г.В., Лялин Г.С. Земляничник мелкоплодный в заповеднике "Мыс Мартьян" // Бюл. Главн. ботан. сада. – 1975. – Вып. 98. – С. 59–63. 11. Ларина Т. Г. Флора и растительность заповедника "Мыс Мартьян" // Труды Гос. Никит. ботан. сада. – 1976. – Т. 70. – С. 45–62. 12. Лукс Ю.А. Флора орхидных заповедника "Мыс Мартьян" // Труды Гос. Никит. ботан. сада. – 1976. – Т. 70. – С. 95–104. 13. Маслов И.И. Фитобентос псевдолиторального пояса района Ялты // Природные экосистемы Южного берега Крыма и их охрана. Сборник науч. тр. – Ялта: ГНБС. – 1984. – Т. 94. – С. 72–87. 14. Маслов И.И., Куропатов Л.А. К детальному описанию биоценоза цистозиры заповедника "Мыс Мартьян". – Бюлл. Гос. Никит. ботан. сада. – 1987. – Вып .63. – С. 13–17. 15. Маслов И.И., Саркина И.С., Белич Т.В., Садогурский С.Е. Аннотированный каталог водорослей и грибов заповедника "Мыс Мартьян". – Ялта, ГНБС. – 1998. – 31 с. 16. Молчанов Е.Ф., Григоров А.Н., Голубева И.В., Ларина Т.Г., Щербатюк Л.К., Ругузов И.А., Склонная Л.У., Бескаравайный М.М. Высокоможжевеловые леса Крыма и проблема их охраны // Гос. Никитск. ботан. сад. – Ялта, 1992. – Деп. В ВИНИТИ 30.12.92. № 3706 – В 92. – 296 с. 17. Погребняк И.И., Маслов И.И. К изучению донной растительности района мыса Мартьян // Труды Гос. Никит. ботан. сада. – 1976. – Т. 70. – С. 105–113. 18. Ходосовцев А.Е., Редченко А.А. Аннотированный список лишайников заповедника "Мыс Мартьян" (Украина) // Укр. ботан. журн. – 2002. – 59, № 1. – С. 64– 71. 19. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Mytrofanivskyi Pivostriv V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Митрофанівський півострів. Transliteraion/Translaion variants: Mytrofanivsky Peninsula. Area: 817.1 ha. Altitude: 0–19 m 206 Latitude: 46°08'27" N (46.1407°). Longitude: 34°07'05" E (34.1181°). Administrative regions. Kherson region: Novotroitske raion . Ownership: state, private. Biogeographic regions: steppic. Habitats. Level 1. A – 16.5%; E – 83.5%. Habitats. Level 2. A2 Littoral sediment – 11.0%; A5 Sublittoral sediment – 5.5%; E1 Dry grasslands – 40.8%; E6 Salt steppes – 42.7%. Futher habitat description. A2.3 Littoral mud; A2.5 Coastal saltmarshes and saline reedbeds; A5.3 Subittoral mud; E1.2 Perennial calcareous grassland and basic steppes; E6.2 Continental inland salt steppes. Land use: nature conservaion and research – minor. Protected areas: included in Ramsar Site "Central Syvash", overlaps (about 218 ha) with Azovo-Syvaskyi naional nature park and Emerald Site "Azovo-Syvaskyi Naional Nature Park". Threats: agricultural intensification/expansion (arable) – low, burning of vegetaion – low. General description. Northern shore of the Central Syvash Bay (saline lagoon of the Sea of Azov). The IPA includes areas with the steppe vegaion, litoral with the halophyic vegetaion and shallow water of the bay. The steppe vegetaion is dominated by Agropyron pecinatum, Artemisia taurica, Festuca valesiaca, Sipa lessingiana, Sipa capillata, Crinitaria villosa. Other typical species are Achillea setacea, Astragalus asper, Astragalus reduncus, Limonium platyphyllum, Linaria macroura, Medicago romanica, Phlomis pungens, Potenilla obscura, Prangos odontalgica. Dominants of the halophyic vegetaion are Halocnemum strobilaceum, Puccinelia fominii, Petrosimonia brachiata, Limonium sufruicosum. A part of the steppe vegetaion is thretened by plowing. Botanical significance. The area includes large parts of global populaions of endemic species Goniolimon rubellum and Lepidium syvaschicum. 207 Criterion A • Goniolimon rubellum (S.G.Gmel.) Klokov; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Lepidium syvaschicum Kleopow; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Conservaion proposals. Include in Azovo-Syvaskyi naional nature park. Literature 1. Коломійчук В.П. Сучасне поширення видів судинних рослин описаних Ю.Д. Клеоповим з Присивашшя // Ю.Д. Клеопов та сучасна ботанічна наука. Мат-ли читань, присвячені 100-річчю з дня народження Ю.Д. Клеопова (Київ, 10–13 листопада 2002 р.). – Київ: Фітосоціоцентр, 2002. – С. 48–51. 2. Павлов В.В. Північне Присивашшя як елемент Азово-Чорноморського екокоридору // Укр. ботан. журн. – 2002. – 59, №1. – С. 89–93. lessingiana. Frequent species are Salvia nutans, Plantago stepposa, Trifolium montanum, Achillea nobilis, Artemisia austriaca, Echium rubrum, Thalictrum minus. Steppic shrub communiies are dominated by Caragana frutex, Amygdalus nana, Spiraea hypericifolia, Cotoneaster melanocarpa. Shale outcrops are characterized by the presence of the local endemic species Scrophularia donetzica. Woods with dominance of Quercus robur, Fraxinus excelior, Tilia cordata and Ulmus laevis are in valleys and gulches. Naholnyi Kriazh V.A. Onyshchenko, M.M. Peregrym Ukrainian name: Нагольний кряж. Transliteraion/Translaion variants: Nagol'nyi Ridge. Area: 3835.0 ha. Altitude: 140–249 m. Latitude: 47°58'48" N (47.9801°). Longitude: 39°29'59" E (39.4996°). Administrative regions. Luhansk region: Dovzansk (Sverdlovsk) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 92.4%; F – 0.5%; G – 1.8%; H – 1.0%; I – 4.3%. Habitats. Level 2. E1 Dry grasslands – 91.4%; E2 Mesic grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 0.5%; G1 Broadleaved deciduous woodland – 1.8%; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.9%; I1 Arable land and market gardens – 4.3%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; I1.5 Bare illed, fallow or recently abandoned arable land; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs; H5.6 Trampled areas. Land use: agriculture (animals) – major; agriculture (arable) – minor; extracion (minerals) – minor; nature conservaion and research – minor. Protected areas: overlaps (about 434 ha) with regional landscape reserve "Naholnyi Kriazh", included in Emerald Site "Naholny Kriazh". Threats: agricultural intensification/expansion (arable) – medium, agricultural intensiicaion/expansion (grazing) – low, extracion (minerals/quarries) – low, forestry (aforestaion) – low. General description. Dry grasslands with small areas of sandstone and shale outcrops, shrubs and deciduous woods. Dominants of the steppe vegetaion are Festuca valesiaca, Bothriochloa ischaemum, Agropyron pectinatum, Poa angusifolia, Sipa capillata, S. 208 Botanical signiicance. A large area of the steppe vegetaion. Criterion A • Hyacinthella pallasiana (Steven) Losinsk.; A(iv); abundance: occasional; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 2800 ha; trend: unknown; area data quality: good; trend data quality: poor Conservaion proposals. Do not allow plowing. Create a state botanical reserve including the enire IPA. Literature 1. Природно-заповідний фонд Луганської області // О.А. Арапов (заг. ред.), Т.B. Сова, О.А. Cавенко, В.Б. Фєрєнц, Н.У. Кравець, Л.Л. Зятьков, Л.О. Морозова. Довідник. – 3-е вид., доп. і перероб. – Луганськ: "Луганська правда", 2013. – 224 с. 209 Novobila V.A. Onyshchenko, M.V. Banik Ukrainian name: Новобіла. Area: 2469.0 ha. Biogeographic regions: steppic. Habitats. Level 1. D – 4.3%; E – 77.2%; F – 2.0%; G – 9.4%; H – 5.1%; I – 2.0%. Habitats. Level 2. D5 Sedge and reedbeds, normally without free-standing water – 4.3%; E1 Dry grasslands – 76.6%; E2 Mesic grasslands – 0.6%; F3 Temperate and mediterraneanmontane scrub – 2.0%; G1 Broadleaved deciduous woodland – 9.4%; H2 Screes – 5.1%; I1 Arable land and market gardens – 2.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – major; forestry – minor; nature conservaion and research – major. Protected areas: overlaps (>2000 ha) with Novobila regional botanical nature monument, overlaps (2214 ha) with Emerald Site "Novobilskyi". Threats: abandonment/reducion of land management – low; agricultural intensification/ expansion (arable) – low, extracion (minerals/quarries) – low; forestry (aforestaion) – low. General description. Slopes with the steppe vegetaion, outcrops of chalk and oak woods; small areas of reedbeds and hay meadows. There are many threatened species of steppes and chalk outcrops. Botanical significance. The largest locality of Hedysarum ucrainicum in Ukraine. Important area for conservaion of the steppes and chalk outcrops with endemic species. Criterion A • Hedysarum ucrainicum Kaschm.; A(iv); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.13 Coninental dry rocky steppic grasslands and dwarf scrub on chalk outcrops; area: 135 ha; trend: stable; area data quality: medium; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 2000 ha; trend: stable; area data quality: good; trend data quality: poor. Literature 1. Banik M. Daphne'04. Final report. – Kharkiv, 2006. – 20 p. (http://www.rufford.org/ files/127.01.04%20Detailed%Final%20Report.pdf). Novohredneve Altitude: 70–160 m. Latitude: 49°47'03" N (49.7841°). Longitude: 39°09'34" E (39.1595°). Administrative regions. Luhansk region: Novopskov raion. Ownership: state. 210 Ukrainian name: Новогредневе. Transliteraion/Translaion variants: Novogredneve. Area: 16.2 ha. Altitude: 7–23 m. Latitude: 47°09'41" N (47.1613°). Longitude: 32°59'52" E (32.9978°). Administrative regions. Kherson region: Velyka Oleksandrivka raion. 211 V.P. Kolomiychuk Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 76.0%; G – 20.0%; H – 2.0%; J – 2.0%. Habitats. Level 2. E1 Dry grasslands – 76.0%; G1 Broadleaved deciduous woodland – 19.0%; G3 Coniferous woodland – 1.0%; H5 Miscellaneous inland habitats with very sparse or no vegetaion – 2.0%; J3 Acive opencast mineral extracion sites, including quarries – 2.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); G1.C Highly artificial broadleaved deciduous forestry plantations; H5.6 Trampled areas; J3.2 Active opencast mineral extraction sites, including quarries. Land use: agriculture (animals) – major, extracion (minerals) – minor, forestry – major. Protected areas: –. Threats: agricultural intensiicaion/expansion (grazing) – low, burning of vegetaion – low, Robinia pseudoacacia, Pinus pallasiana, Ulmus minor. Illegal sand quarry occupies a small part of the site. Botanical significance. Important area for narrow endemic species Centaurea paczoskii (one of 2 localiies). Criterion A • Centaurea paczoskii Kotov ex Klokov; A(iii); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Remove trees. Create a state botanical reserve and an Emerald Site including the enire IPA. Literature 1. Крицька Л.І., Деркач О.М. Сучасний стан популяцій видів ряду Margaritaceae Klok. (Centaurea L.) // Укр. ботан. журн. – 1991. – 48, № 3. – С. 78 – 80. 2. Мойсієнко І.І., Мельник Р.М. Волошка Пачоського Centaurea paczoskii Klokov (C. margaritacea Ten. subsp. paczoskii (Kotov et Klokov) Dostál) / Червона книга України. рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – С. 306. Nyzhnii Dnipro extracion (mineral/quarries) – medium, forestry (aforestaion) – low. General description. Grassland on the sand terrace of the Inhulets river. Dominant species are Carex colchica, Festuca beckeri, Artemisia campestris. Other frequent species are Eragrostis minor, Chondrilla juncea, Dianthus platyodon, Jurinea sp., Helichrysum arenarium, Koeleria glauca s.l., Plantago scabra. Moss layer consists of Tortula ruralis (cover 3–10%). Populaion of Centaurea paczoskii occupies 2–3 ha. A part of the area is ariicial wood with 212 V.A. Onyshchenko Ukrainian name: Нижній Дніпро. Transliteraion/Translaion variants: Lower Dnipro, Lower Reaches of the Dnieper. Area: 43083.0 ha. Altitude: 0–13 m. Latitude: 46°36'01" N (46.6004°). Longitude: 32°38'46" E (32.6461°). Administrative regions. Kherson region: Beryslav raion, Biloozerka raion, Hola Prystan raion, Oleshky (Tsiurupynsk) raion, Kherson city; Nova Kakhovka city . Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 30.4%; D – 55.5%; E – 4.2%; F – 0.4%; G – 9.5%. Habitats. Level 2. C1 Surface standing waters – 14.5%; C2 Surface running waters – 13.8%; C3 Littoral zone of inland surface waterbodies – 2.1%; D5 Sedge and reedbeds, normally without free-standing water – 55.5%; E3 Seasonally wet and wet grasslands – 3.9%; E6 Inland salt steppes – 0.3%; F9 Riverine and fen scrubs – 0.4%; G1 Broadleaved deciduous woodland – 8.3%; G3 Coniferous woodland – 1.2%. Futher habitat descripion. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-idal, smooth-lowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; E6.2 Coninental inland salt steppes; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.3 Mediterranean riparian woodland; G3.F Highly ariicial coniferous plantaions. Land use: forestry – 10%; mowing/hay making – minor, urban/industrial/transport – minor, tourism/recreaion – minor. Protected areas: overlaps with Nyzhniodniprovskyi naional nature park (about 40000 ha), 213 overlaps (39039 ha) with Emerald Site "Lower Dnipro", overlaps (3823 ha) with Emerald Site "Dniprovsko-Buzkyi Lyman", overlaps (123 ha) with Emerald Site "Kinburnska Kosa". Threats: development (recreaion/tourism) – low, development (urbanizaion) – low. General descripion. Floodplain of the Dnipro river from Nova Kakhovka to the mouth. Phragmites australis dominated marshes occupy the largest area. Other important dominants are Typha angusifolia, Carex acuiformis, Carex elata. Large areas are occupied by aquaic vegetaion dominated by Ceratophyllum demersum, Lemna minor, Myriophyllum • C2.34 Eutrophic vegetation of slow-flowing rivers; area: 300 ha; trend: stable; area data quality: poor; trend data quality: medium. • D5.2 Beds of large sedges normally without free-standing water; area: 400 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Дубына Д.В., Шеляг-Сосонко Ю.Р. Плавни Причерноморья. – К.: Наук. думка, 1989. – 272 с. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 3. Чинкіна Т.Б. Сучасний стан і завдання охорони рослинного покриву гирлової області Дніпра // Природничий альманах. Сер. біол. науки, 2002. – Вип. 2(3). – С. 240–247. 4. Чинкіна Т. Синтаксономічна схема заплавної рослинності гирлової ділянки Дніпра // Вісник Львівського університету. Сер. біол., 2006. – 42. – С. 32–37. Nyzhniodniprovski Pisky vericillatum, Myriophllum spicatum, Nuphar lutea, Nymphaea alba, Potamogeton pecinatus (Stuckenia pecinata), Potamogeton perfoliatus, Potamogeton crispus, Potamogeton berchtoldii, Salvinia natans, Spirodela polyrrhiza. Woods cover about 4000 ha. Main dominant is Salix alba, other important species – Salix fragilis, Populus alba, Populus nigra. Shrub vegetaion is represented mainly by communiies of Salix cinerea, Salix triandra, Salix acuifolia. Botanical significance. This area is one of the richest in aquaic vascular plant species in Ukraine. Criterion A • Carex secalina Wahlenb.; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Salvinia natans (L.) All.; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. • Trapa natans L.; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • C1.224 Floaing Utricularia australis and Utricularia vulgaris colonies; area: 3 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.225 Floaing Salvinia natans mats; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.3411 Ranunculus communities in shallow water; area: 1 ha; trend: unknown; area data quality: poor; trend data quality: poor. V.A. Onyshchenko Ukrainian name: Нижньодніпровські піски. Transliteraion/Translaion variants: Lower Dnipro Sands. Area: 10388.0 ha. Altitude: 0–10 m. Latitude: 46°27'21" N (46.4559°). Longitude: 31°58'28" E (31.9744°). Administrative regions. Kherson region: Hola Prystan raion; Mykolaiv region: Ochakiv raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 1.6%; C – 16.0%; D – 1.6%; E – 67.8%; F – 1.0%; G – 10.0%; H – 2.0%. Habitats. Level 2. A2 Littoral sediment – 0.2%; A5 Sublittoral sediment – 1.4%; C1 Surface standing waters – 16.0%; D5 Sedge and reedbeds normally without free-standing water – 1.5%; D6 Inland saline and brackish marshes and reedbeds – 0.1%; E1 Dry grasslands – 58.7%; E2 Mesic grasslands – 5.4%; E3 Seasonally wet and wet grasslands – 2.3%; E6 Inland salt steppes – 1.4%; F3 Temperate and mediterranean-mountane scrub – 1.0%; G1 Broadleaved deciduous woodland – 10.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 2.0%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes, E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland, (× E1.1) E2.5 Meadows of the steppe zone, E3.4 Moist or wet eutrophic and mesotrophic grassland, F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland, G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia, H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity. Land use: nature conservation and research – major, agriculture (animals) – minor. Protected areas: overlaps (5397 ha) with Chernomorskiy (Chornomorskyi, Black Sea) biosphere reserve (UNESCO, core zone of the reserve), overlaps (5397 ha) with Chornomorskyi biosphere reserve (naional category), overlaps (ca. 270 ha) with Biloberezhia Sviatoslava 214 215 naional nature park, overlaps with Emerald Sites "Black Sea Biosphere Reserve" (5397 ha), "Biloberezhzhia Sviatoslava Naional Nature Park" (267 ha), "Kinburnska Kosa" (4724 ha). Threats: forestry (afforestation) – low. General description. Major habitat type is the dry sand grassland. Other habitats are sublittoral of Kinburn (Yahorlytska) Bay, mesic grasslands, beds of Carex riparia and Carex elata, halophytic vegetation, deciduous woods (small groves), freshwater and saline permanent and temporary lakes. Sand grasslands are dominated by Festuca beckeri, Koeleria sabuletorum, Agropyron lavrenkoanum, Stipa borysthenica, Artemisia marschalliana. Their typical species are Achillea micrantha, Agropyron dasyanthum, Anchusa gmelinii, Asperula graveolens, Dianthus platyodon, Helichrysum corymbiforme, Jacobaea borysthenica (Senecio borysthenicus), Scabiosa ucrainica, Scorzonera ensifolia, Seseli tortuosum, Tragopogon borysthenicus. Dominants of the mesic grasslands are Agrostis sabulicola, Calamagrosts epigeios, Cynodon dactylon, Elytrigia elongata, Elytrigia repens, Phleum phleoides, Poa angustifolia. Typical species: Achillea euxina, Allium guttatum, Campanula rapunculus, Carex melanostachya, Centaurea adpressa, Festuca rupicola, Hypericum perforatum, Inula sabuletorum, Linum perenne, Rumex acetosella, Rumex thyrsiflorus, Veronica steppacea. Puccinellia gigantea dominates in saline grasslands. Other frequent halophyic specis are Aeluropus littoralis, Juncus gerardii, Limonium meyeri, Scorzonera parviflora, Spergularia marina. Woods are represented by groves of Quercus robur, Betula borysthenica, Populus tremula. Quercus robur woods have the shrub layer (0.2–0.4) consisting of Rhamnus catharctica, Sambucus nigra, Crataegus fallacina, Crataegus alutacea. The most frequent species of the herb layer are Acillea euxina, Asparagus tenuifolius, Calamagrostis epigeios, Carex elata, Convallaria majalis, Dactylis glomerara, Elytrigia repens, Phragmites australis, Poa sylvicola, Polygonatum odoratum, Scilla bifolia, Viola odorata. The most frequent species of Betula borysthenica woods: Agrostis sabulicola, Calamagrostis epigeios, Carex elata, Frangula alnus, Genista borysthenica, Genista sibirica, Hieracium umbellatum, Juncus atratus, Juncus conglomeratus, Phragmites australis, Rhamnus cathartica, Rubus caesius, Salix rosmarinifolia, Solidago virgaurea. The most frequent species of Populus tremula woods: Carex elata, Euphorbia semivillosa, Frangula alnus, Lysimachia vulgaris, Phalaroides arundinacea, Rubus caesius, Sambucus nigra, Veronica longifolia. Littoral vegetation of 216 lakes is dominated by Phragmites australis, aquaic vegetaion of lakes by Lemna minor and Lemna trisulca. Botanical significance. The best area of sand steppe in Ukraine. Criterion A • Agropyron dasyanthum Ledeb.; A(i); abundance: frequent; trend: stable; species data quality: medium; trend data quality: poor. • Allium savranicum Besser; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Alyssum savranicum Andrz. ex Besser (Odontarrhena savranica (Andrz. ex Besser) D.A.German); A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Centaurea breviceps Iljin; A(iii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Goniolimon graminifolium (Ait.) Boiss.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor Criterion C • E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; area: 6000 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Do not allow ariicial aforestaion. Literature 1. Андрієнко Т.Л., Кофман І.Ш., Уманець О.Ю., Якушина Л.А. Розподіл рослинності та її антропогенні зміни на Івано-Рибальчанській ділянці Чорноморського біосферного заповідника // Укр. ботан. журн. – 1992. – 49, № 2. – С. 22–25. 2. Соломаха І.В., Воробйов Є.О., Мойсієнко І.І. Рослинний покрив лісів та чагарників Північного Причорномор’я. – К.: Фітосоціоцентр, 2015. – 387 с. 3. Ткаченко В.С., Лисенко Г.М., Маяцький Г.Б., Уманець О.Ю. Структурні зміни фітоценокомплексів Солоноозерної ділянки Чорноморського біосферного заповідника за даними періодичного картографування // Укр. ботан. журн. – 1997. – 54, № 3. – С. 232–239. 4. Ткаченко В.С., Уманець О.Ю. Фітоценотична характеристика Солоноозерної ділянки Чорноморського біосферного заповедника (Херсонська область, Україна) // Укр. ботан. журн. – 1993. – 50, № 2. – С. 14–23. 5. Уманець О.Ю. БЗ Чорноморський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 73–93. 6. Уманець О.Ю., Соломаха І.В. Синтаксономія рослинності Чорноморського біосферного заповідника. III. Ділянка Івано-Рибальчанська // Укр. фітоцен. зб. – Київ, 1999. – Сер. А, вип. 3 (14). – C. 84–102. 217 Obyichna Kosa V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Обитічна коса. Transliteraion/Translaion variants: Obyichna Spit, Obitochna Spit. Area: 4738.1 ha. Altitude: 0–2 m. Latitude: 46°34’10” N (46.5693°). Longitude: 36°14’00” E (36.2332°). Administrative regions. Zaporizhia region: Prymorsk raion. Territorial waters of Ukraine. Ownership: state (major), private. Biogeographic regions: steppic. Habitats. Level 1. A– 49.1%; B – 1.7%; C – 9.7%; D – 0.5%; E – 36.7%; G – 2.3%. Habitats. Level 2. A2 Littoral sediment – 5.3%; A5 Sublittoral sediment – 43.8%; B1 Coastal dunes and sandy shores – 1.0%; B2 Coastal shingle – 0.7%; C1 Surface standing waters 218 – 9.7%; D6 Inland saline and brackish marshes and reedbeds – 0.5%; E1 Dry grasslands – 34.2%; E6 Salt steppes – 2.5%; G1 Broadleaved deciduous woodland – 2.3%. Futher habitat description. A2.1 Littoral coarse sediment; A2.2 Littoral sand and muddy sand; A2.4 Littoral mixed sediments; A2.5 Coastal saltmarshes and saline reedbeds; B1.1 Sand beach driftlines; B1.2 Sand beaches above the driftline; B1.3 Shifting coastal dunes; B1.4 Coastal stable dune grassland (grey dunes); B2.1 Shingle beach driftlines; B2.2 Unvegetated mobile shingle beaches above the driftline; C1.5 Permanent inland saline and brackish lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E1.2 Perennial calcareous grassland and basic steppes (E1.2G); E6.2 Coninental inland salt steppes; G1.C Highly ariicial broadleaved deciduous forestry plantations. Land use: forestry – minor; hunting – minor; mowing/hay making – 2%; nature conservation and research – major. Protected areas: included in Kosa Obyichna state landscape reserve, includes Ramsar Site “Obytochna Spit and Obytocna Bay”, overlaps (about 4708 ha) with Emerald ste “Obyichna Kosa Ta Zatoka”. Threats: climate change/ sea level rise – low, development (recreaion/tourism) – low, forestry (aforestaion) – low, natural events: spit erosion – medium General description. A spit composed of shells and sand with adjacent sea. Major aquaic species are Zostera marina, Zostera nolii (Nanozostera nolii), Potamogeton pecinatus (Stuckenia pecinata), Zanichellia major. Litoral vegetaion of the Sea of Azov and saline lakes is represented by halophyic communiies dominated by Phragmites australis, Juncus mariimus, Salicornia perennans. On sand, there prevail Leymus sabulosus, Carex colchica, Crambe mariima, Festuca beckeri, Medicago kotovii; other typical species are Artemisia santonica, Centaurea adpressa, Centaurea odessana, Euphorbia seguierana. Botanical significance. Important area for conservaion of sand steppes and brackish aquaic vegetaion. Criterion A • Zostera marina L.; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • B1.1 Sand beach driftlines; area: 6 ha; trend: stable; area data quality: medium; trend data quality: medium. • E1.2 Perennial calcareous grassland and basic steppes; area: 850 ha; trend: decreasing; area data quality: medium; trend data quality: medium. Literature 1. Коломійчук В.П. Флора і рослинність островів Обитічної затоки // Укр. ботан. журн. – 2000. – 57, № 2. – С. 134–141. 2. Коломійчук В.П. Ключові ботанічні території Північного Приазов’я // Заповідна справа в Україні. – 2008. – Т. 14, вип. 1. – С. 61–66. 3. Ткаченко В.С., Кучерява Л.Ф., Тищенко О.В. Багаторічні зміни та сучасний стан рослинності Обитічної коси // Укр. ботан. журн. – 1998. – 55, № 6. – С. 639–647. 4. Тищенко О.В. Рослинність приморських кіс північного узбережжя Азовського моря. – Київ: Фітосоціоцентр, 2006. – 156 с. 219 Olevski Lisy Ukrainian name: Олевські ліси. Transliteraion/Translaion variants: Olevskyi Forest. Area: 4930.0 ha. Altitude: 182–190 m. Latitude: 51°17’17” N (51.2879°). Longitude: 27°30’15” E (27.5042°). Administrative regions. Zhytomyr region: Olevsk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 0.4%; F – 1.0%; G – 97.6%; H – 1.0%. O.O. Orlov Habitats. Level 2. D2 – Valley mires, poor fens and transition mires – 0.4%; F9 Riverine and fen scrubs – 1.0%; G1 Broadleaved deciduous woodland – 38.3%; G3 Coniferous woodland – 29.0%; G4 Mixed deciduous and coniferous woodland – 26.6%; G5.6 Early-stage natural and semi-natural woodlands and regrowth – 3.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. D2.3 Transition mires and quaking bogs; F9.2 Salix carr and fen scrub; G1.5 Broadleaved swamp woodland on acid peat; G1.8 Acidophilous Quercusdominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus 220 aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice; H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – 20%. Protected areas: overlaps (about 1000 ha) with Banky regional forest reserve. Threats: forestry (intensiied forest management) – low. General description. Acidophilous Pinus sylvestris, Quercus robur, Betula pendula woods, neutrophilous Quercus robur – Carpinus betulus woods, and Betula pubescens swamps. Dominants of the wet pine woods are Franula alnus, Molinia caerulea, Pteridium aquilinum, Vaccinium myrillus, Dicranum polysetum, Pleurozium shreberi. Other frequent species are Dryopteris carthusiana, Trientalis europaea (Lysimachia europaea), Vaccinium uliginosum, Vaccinium viis-idaea. On the drier soils, there are species-rich Pinus sylvestris woods with dominance of Rhododendron luteum. Dominants of the herb layer are Convallaria majalis and Pteridium aquilinum. Constant species: Calamagrosis arundinacea, Carex montana, Galium intermedium, Maianthemum bifolium, Polygonatum odoratum, Primula veris, Serratula coronata. Diferenial species of the swamped pine woods are Andromeda polifolia, Carex nigra, Ledum palustre, Sphagnum fallax, Sphagnum palustre. In acidophilous Quercus robur woods, there are the shrub layer consising of Frangula alnus. The herb layer is dominanted by Anemone nemorosa, Luzula pilosa, Lysimachia vulgaris, Oxalis acetosella. On the richer soil, there are Quercus robur – Carpinus betulus woods dominated by Anemone nemorosa, Asarum europaeum, Milium efusum, Aegopodium podagraria, Galium odoratum, Lamium galeobdolon, Pulmonaria obscura, Viola reichenbachiana. Botanical significance. Important for conservaion of Rhododendron lutem and acidophilous oak forests. Criterion A • Rhododendron luteum Sweet; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Literature 1. Орлов О.О., Сіренький С.П., Якушенко Д.М., Жижин М.П., Степаненко М.А., Тарасевич О.В. Природно-заповідний фонд Житомирської області. Довідник / За заг. ред. О.О. Орлова. – Житомир – Новоград-Волинський: Вид-во НОВОград, 2015. – 404 с. 2. Орлов О.О., Якушенко Д.М., Воробйов Є.О. Флористична класифікація лісів із участю Rhododendron luteum Sweet та радіоекологічна оцінка їх асоціацій в Поліссі України. І. Синтаксономія лісів із участю Rhododendron luteum // Укр. фітоцен. зб. – 2000. - Серія А, Вип. 1 (16). – Київ: Фітосоціоцентр. – С. 94–113. Opuk V.A. Onyshchenko Ukrainian name: Опук. Area: 2070.0 ha. Altitude: 0–184 m. Latitude: 45°02’35” N (45.0429°). Longitude: 36°12’37” E (36.2103°). 221 Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 24.9%; B – 0.7%; C – 32.0%; D – 0.5%; E – 41.5%; H – 0.4%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.1%; A2 Littoral sediment – 0.5%; A3 Infralittoral rock and other hard substrata – 4.1%; A5 Sublittoral sediment – 20.1%; B1 Coastal dunes and sandy shores – 0.3%; B2 Coastal shingle – 0.2%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.1%; C1 Surface standing waters – 32.0%; D6 Inland saline and brackish marshes and reedbeds – 0.5%; E1 Dry grasslands – 39.9%; E2 – Mesic grasslands – 1.5%; E6 Inland salt steppes – 0.1%; H2 Screes – 0.01%; H3 Inland clifs, rock pavements and outcrops – 0.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.1 Litoral coarse sediment; A2.2 Litoral sand and muddy sand; A5.4 Sublitoral mixed sediments; A5.5 Sublitoral macrophyte-dominated sediment; A2.5 Coastal saltmarshes and saline reedbeds; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.5 Sublitoral macrophytedominated sediment; B1.1 Sand beach dritline; B1.2 Sand beaches above the dritline; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; C1.5 Permanent inland saline and brackish lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; D6.1 Inland saltmarshes; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E1.3 Mediterranean xeric grassland; E2.7 Unmanaged mesic grassland; E6.2 Coninental inland salt steppes; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: nature conservation and research – 77%. Protected areas: includes Opukskyi nature reserve (1592.3 ha) and Emerald Site “Opukskyi Nature Reserve” (1592.3 ha). Threats: –. General description. The IPA includes Opuk Hill (184 m over the sea level), salt Lake Koyash (Koyaske) and adjacent part of the Black Sea. The steppe vegetaion occupies the largest area, usually it is on shallow stony solis; dominants: Sipa capillata, Sipa pulcherrina, Festuca rupicola, Festuca valesiaca, Koeleria cristata; typical species: Achillea setacea, Artemisia taurica, Asperula kotovii, Bromopsis cappadocica, Euphorbia seguierana, Filipendula vulgaris, Galium tenuissimum, Galium verum, Medicago glandulosa, Phleum phleoides, Teucrium chamaedrys, Teucrium polium. On limestone outcrops, typical species are Euphorbia petrophila, Minuaria hypanica, Pimpinella lithophila, Thymus callieri. Salinity of Lake Koyash is 160–350‰. In summer the lake is the most saline and its peripheral part is dry. There no macrophytes in aquaic vegetaion in the lake excluding the southern part where there is iniltraion of less saline sea water; saltmarshes are dominated mainly by Halocnemum strobilaceum with presence of Limonium caspium, Suaeda salsa, Puccinellia distans, Salicornia perennans. Near the sea, there occur communiies of Crambe mariima, Eryngium mariimum, Leymus racemosus, Phragmites australis, Juncus mariimus, Elytrigia elongata, Aeluropus litoralis. In the sea on hard substrates near capes, there prevail Ceramium rubrum, Cladostephus vericillatus, Corallina granifera, Cystoseira barbata, Cystoseira crinita, Dilophus fasciola, Gelidium crinale, Gelidium laifolium, Polysiphonia subulifera. In bays, Enteromorpha intesinalis and Ceramium ciliatum dominates. On pebble beach and boulders near the sea, there dominate Crithmum mariimum and Elytrigia bessarabica; on the slopes of Opuk Hill near the sea, there are communiies of Halimione verrucifera, Holosteum umbellatum, Kochia prostrata. Botanical significance. Important area for conservaion of the steppe vegetaion, sea clifs, and marine macrophytes. Criterion A • Crambe aspera M.Bieb.; A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Crambe koktebelica (Junge) N.Busch; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe mitridais Juz.; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Thymus litoralis Klokov et Des.-Shost.; A(iii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • A3 Infralittoral rock and other hard substrata; area: 40 ha; trend: stable; area data quality: poor; trend data quality: poor. • A5 Sublitoral sediment; area: 400 ha; trend: stable; area data quality: medium; trend 222 223 data quality: good. B3.3 Rock cliffs, ledges and shores, with angiosperms; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Белич Т.В., Садогурская С.А., Садогурский С.Е. Аннотированный список фитобентоса Опукского природного заповедника // Труды Никит. ботан. сада. – 2006. – Т. 126. – С. 74–88. 2. Исиков В.П. Опукский природный заповедник // Сборник тр. Никит. ботан. сада.– 2001. – С. 13–27. 3. Корженевский В.В., Рыфф Л.Э. Анализ флоры высших сосудистых растений Опукского природного заповедника // Труды Никит. Ботан. сада. – 2006. – Т. 126. – С. 51–73. 4. Корженевский В.В., Садогурський С.Ю., Квітницька О.І. ПЗ Опукський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 291–300. 5. Маслов И.И. Макрофитобентос некоторых заповедных акваторий Черного моря (Украина) // Альгология. – 2002. – Т. 12, № 1. – С. 81–95. 6. Новосад В.В. Флора Керченско-Таманского региона. – Киев: Наукова думка, 1992. – 278 с. 7. Пузанов И.И. По нехоженому Крыму. – М.: Географгиз, 1960. – 270 с. 8. Садогурская С.А. Cyanophyta морской каменистой супралиторали Крыма: Дис. … канд. биол. наук: 03.00.05 – Ялта, 2005. – 395 с. 9. Садогурский С.Е., Белич Т.В. Макрофитобентос Опукского природного заповедника (Черное море) // Мат-лы науч. конф., посв. 180-летию заслуженного проф. Харьковского ун-та Л.С.Ценковского (Харьков, 4–5 декабря, 2002 г.). – Харьков, 2003. – С. 65–67. 10. Садогурский С.Е. Белич Т.В. Современное состояние макрофитобентоса Опукского природного заповедника (Черное море) // Альгология. – 2003. – 13, № 2 – С. 185–203. 11. Садогурский С.Е., Белич Т.В., Садогурская С.А., Маслов И.И. Видовой состав фитобентоса природных заповедников Крыма // Бюлл. ГБС РАН. – 2003. – Вып. 186. – С. 86–104. • Habitats. Level 1. E – 78.6%; F – 2.0%; G – 9.6%; H – 9.8%. Habitats. Level 2. E1 Dry grasslands – 78.6%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 9.6%; H2 Screes – 9.8% Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures. Oskilski Skhyly V.A. Onyshchenko, O.V. Bezrodnova, M.V. Banik Ukrainian name: Оскільські схили. Transliteraion/Translaion variants: Oskil Slopes. Area: 1525.0 ha. Altitude: 80–180 m. Latitude: 49°57’39” N (49.9609°). Longitude: 37°48’06” E (37.8017°). Administrative regions. Kharkiv region: Dvorichna raion. Ownership: state. Biogeographic regions: steppic. Land use: agriculture (animals) – major; nature conservaion and research – major. Protected areas: overlaps (1067 ha) with Dvorichanskyi naional nature park, includes Chervonyi regional botanical reserve (49.8 ha), includes Korobochkine regional botanical reserve (29.1 ha), includes Kreidianyi regional botanical reserve (36.9 ha), includes Konopliane regional botanical reserve (315.9 ha), overlaps (1067 ha) with Emerald Site “Dvorichanskyi Naional Nature Park”. 224 225 Threats: abandonment/reducion of land management – low; burning of vegetaion – medium; extracion (minerals/quarries) – low; forestry (aforestaion) – low. General description. Slopes with outcrops of chalk, steppes, oak forests. Dominants of communiies on chalk are Asperula tephrocarpa, Bupleurum falcatum, Thymus calcareus, less frequently – Artemisia hololeuca, Astragalus albicaulis, Carex humilis, Cephalaria uralensis, Hyssopus cretaceus, Koeleria talievii, Linum ucrainicum, Onosma tanaiica, Scrophularia cretacea; locally – Artemisia salsoloides, Hedysarum grandilorum. Other typical species are Androsace koso-poljanskii, Helianthemum cretaceum, Astragalus austriacus, Erucastrum cretaceum, Euphorbia seguieriana, Genista tanaitica, Gypsophila alissima, Mathiola fragrans, Meniocus linifolius, Odontites luteus, Polygala cretacea, Polygala sibirica, Silene supina, Teucrium polium. Steppe vegetaion is dominated by Bromopsis riparia, Bromopsis inermis, Festuca valesiaca, Koeleria cristata, Poa angusifolia, Salvia nutans, Sipa capillata, Sipa lessingiana, locally – Sipa pennata, Sipa pulcherrima. There occur steppes with dominance of shrubs (Caragana frutex, Chamaecyisus austriacus, Chamaecyisus tuthenicus). Typical species of the steppe vegetaion are also Adonis vernalis, Clemais integrifolia, Euphorbia stepposa, Galatella villosa, Galatella linosyris, Jurinea calcarea, Teucrium polium, Thalictrum minus, Vinca herbacea. Shrub vegetaion is formed by Cerasus fruicosa, Crataegus sp., Euonymus verrucosus, Malus sylvestris, Prunus spinosa, Rhamnus catharica, Rosa sp., Swida sanguinea (Cornus sanguinea), Ulmus minor. In the tree layer of forests, there dominate Quercus robur, Fraxinus excelsior, Acer campestre, Tilia cordata. The herb layer is dominated by Aegopodium podagraria, Stellaria holostea. Botanical significance. Important area for conservaion of endemic species of chalk outcrops. Criterion A • Alyssum gymnopodum P.A.Smirn. (Odontarrhena gymnopoda (P.A.Smirn.) D.A.German); A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. • Androsace koso-poljanskii Ovcz.; A(iv); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. • Diplotaxis cretacea Kotov; abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Erysimum ucrainicum J.Gay.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.13 Coninental dry rocky steppic grasslands and dwarf scrub on chalk outcrops; area: 120 ha; trend: unknown; area data quality: medium; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 1200 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Безроднова О.В. Раритетные кальцефильные виды в Гербарии Харьковского национального университета имени В. Н. Каразина (CWU) //Вісник Харківського національного університету імені В.Н. Каразіна. Серія: біологія. – 2015. Вип. 25. – С. 16–26. 2. Савченко Г.О., Банік М.В. Ронкін В.І. Червонокнижні види судинних рослин степів і виходів крейди національного природного парку “Дворічанський” та його околиць // Рідкісні рослини і гриби України та прилеглих територій: реалізація природоохоронних стратегій. Матеріали IV Міжнар. конф. 16-20 травня 2016 р. Київ. – К.: друкарня А.В. Паливоди, 2016. – С. 133-136. 226 3. Саідахмедова Н.Б., Банік М.В., Громакова А.Б., Кривохижа М.В. НПП Дворічанський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 191–205. 4. Ткаченко В.С., Парахонська Н.О., Горєлова Л.М. Ботанічний заказник для охорони природної рослинності Поосколля // Укр. ботан. журн. – 1986. – 43, № 6. – С. 59–63. 5. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Osovynskyi Step V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Осовинський степ. Transliteraion/Translaion variants: Osovynskyi Steppe. Area: 5613.0 ha. Altitude: 0–164 m. Latitude: 45°25’58” N (45.4327°). Longitude: 36°28’51” E (36.4807°). Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state (major), private. Biogeographic regions: steppic. Habitats. Level 1. A – 3.2%; B – 0.6%; D – 0.1%; E – 89.3%; F – 4.2%; G – 0.6%; H – 1.0%; I – 1.0%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.0%; A2 Littoral sediment – 227 0.2%; A3 Infralittoral rock and other hard substrata – 0.0%; A5 Sublittoral sediment – 2.9%; B1 Coastal dunes and sandy shores – 0.2%; B2 Coastal shingle – 0.4%; B3 Rock clifs, ledges and shores, including the supralittoral – 0.0%; D6 inland saline and brackish marshes and reedbeds – <0.1%; E1 Dry grasslands – 89.3%; E6 Salt steppes – <0.1%; F3 Temperate and mediterranean-montane scrub – 4.2%; H3 Inland clifs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.9%; I1 Arable land and market gardens – 1.0%. Futher habitat description. A2.1 Litoral coarse sediment; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.4 Sublitoral mixed sediments; B1.2 Sand beaches above the dritline; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); D6.1 Inland saltmarshes; E1.1 Inland sand and rock with open vegetaion; E1.2 Perennial calcareous grassland and basic steppes (>80% of the IPA); E6.2 Continental inland salt steppes; F3.2 Submediterranean deciduous thickets and brushes; G1.C Highly ariicial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas, I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – minor, mowing/hay making – minor, nature conservaion and research – minor, tourism/recreaion – minor. Protected areas: includes regional landscape reserve “Osovynskyi Step” (3472 ha), regional geological nature monuments “Hriaziova Sopka Vernadskoho” (1.0 ha), “Hriazova Sopka Andrusova (1.0 ha), “Hriazova Sopka Obrucheva” (1.0 ha), overlaps (5433 ha) with Emerald Site (“Karalarskyi”). Threats: agricultural intensiicaion/expansion (general) – low, burning of vegetaion – low, development (recreaion/tourism) – low, development (urbanization) – low. General description. Major habitat type is the steppe. Dominant species are Festuca valesiaca, Dactylis glomerata, Stipa brauneri, S. capillata, Agropyron pecinatum, Elytrigia intermedia, E. elongata, Melica transsilvanica, Galatella villosa. The most typical species with lower cover are Achillea setacea, Carduus uncinatus, Centaurea salonitana, Malabaila graveolens, Phlomis pungens, Potenilla obscura. There are shrub communiies with prevailing of Rosa corymbifera, R. lapidosa, R. lupulina, R. pygmaea, R. tesquicola, Crataegus dipyrena, C. stevenii, C. taurica. On slopes to the sea, there are small groves of Ulmus minor. In their herb layer, Anacamptis pyramidalis, Arum elongatum, Corydalus paczoskii, Оrchis purpurea, O. picta, Pisum elatius, Scilla bifolia, Viola suavis occur. In ravines and near mud volcanos there are halophic communiies with predominance of Lepidium crassifolium, Petrosimonia brachiata, Petrosimonia opposiifolia, Puccinellia fominii, Artemisia santonica, Eremopyrum triiceum. Botanical significance. One of the largest areas of the steppe vegetaion in Ukraine. One of the most important areas for Crambe grandilora and Crambe steveniana. Criterion A • Crambe grandilora DC.; A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Crambe steveniana Rupr.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 4300 ha; trend: stable; 228 • area data quality: medium; trend data quality: poor. F3.247 Ponto-Sarmatic deciduous thickets; area: 50 ha; trend: unknown; area data quality: medium; trend data quality: poor. Pecheniiske Boloto V.A. Onyshchenko, O.T. Kuzyarin Ukrainian name: Печенійське болото. Transliteraion/Translaion variants: Pecheniiske Mire. Area: 684.0 ha. Altitude: 234–250 m. Latitude: 49°46’09” N (49.7692°). Longitude: 24°21’12” E (24.3532°). Administrative regions. Lviv region: Pustomyty raion, Zolochiv raion. Ownership: state, private Biogeographic regions: coninental. Habitats. Level 1. C – 0.7%; D – 50.0%; E – 44.3%; F – 2.0%; G – 3.0%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.6%; E2 Mesic grasslands – 1.3%; E3 Seasonally wet and wet grasslands – 39.7%; E5 Woodland fringes and clearings and tall forb stands – 3.3%; D4 Base-rich fens and calcareous spring mires – 30.0%; D5 Sedge and reedbeds, normally without freestanding water – 20.0%; F9 Riverine and fen scrubs – 2.0%; G1 Broadleaved deciduous woodland – 3.0%. Futher habitat descripion. D4.1 Rich fens, including eutrophic tall-herb fens and calcareous 229 flushes and soaks; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E2.2 Low and medium altitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tallherb and fern fringes and meadows; F9.2 Salix carr and fen scrub. Land use: mowing/hay making – minor. Protected areas: –. Threats: abandonment/reducion of land management – low, agricultural intensiicaion/ expanion (general) – medium, water (drainage) – low. General description. Parially drained fen. Major vegetaion types are rich fens and wet grasslands. Dominant species of rich fens are Carex davalliana, Carex lava, Cladium mariscus, Molinia caerulea, Pragmites australis, Schoenus ferrugineus. Other frequent species are Carex lacca, Carex panicea, Equisetum palustre, Lycopus europaeus, Lysimachia vulgaris, Lythrum salicaria, Potenilla anserina, Potenilla erecta, Salix cinerea. Meadows are dominated by Deschampsia cespitosa, Filipendula ulmaria, Molinia caerulea. Botanical significance. One of the largest rich fens in Ukraine with a large populaion of Pedicularis sceptrum-carolinum. Criterion C • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; area: 200 ha; trend: stable; area data quality: poor; trend data quality: medium. Conservaion proposals. Do not allow recovery of reclamaion ditches, create a state reserve, create an Emerald Site. Literature 1. Кузярін О.Т. Перспективні природоохоронні території басейну верхів’я Західного Бугу // Наукові записки державного природохнавчого музею. – Львів. – 2012. – Вип. 28. – С. 121–130. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Futher habitat description. D1.1 Raised bogs; D2.3 Transition mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.7 Closed non-Mediterranean dry acid and neutral grassland; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; F9.2 Salix carr and fen scrub; G1.5 Broadleaved swamp woodland on acid peat; G1.9 Nonriverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland, G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland. Land use: nature conservation and research – major%. Perebrody V.A. Onyshchenko, O.I. Pryadko Ukrainian name: Переброди. Area: 21103 ha. Altitude: 135–145 m. Latitude: 51°41’51” N (51.6974°). Longitude: 27°05’45” E (27.0957°). Administrative regions. Rivne region: Dubrovytsia raion, Rokytne raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. C – 0.5%; D – 60%; E – 0.1%; F – 1%; G – 38.4%. Habitats. Level 2. C1 Surface standing waters – 0.4%; C3 Littoral zone of inland surface waterbodies – 0.1%; D1 Raised and blanket bogs – 1%; D2 – Valley mires, poor fens and transition mires – 39%; D5 Sedge and reedbeds, normally without free-standing water – 20%; E1 Dry grasslands – 0.1%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 10%; G3 Coniferous woodland – 18.4%; G4 Mixed deciduous and coniferous woodland – 10%. Protected areas: overlaps (13460 ha) with Rivnenskyi nature reserve, Emerald Sites “Dubrovytsko-Sarnynskyi” (3719 ha) and “Rivnenskyi Nature Reserve” (13460 ha). Threats: –. General description. One of the largest mires in Ukraine. Major vegetaion type is Carex lasiocarpa and Carex rostrata mires with a peat moss layer (Sphagnum centrale, S. fallax, S. lexuosum, S. magellanicum, S. obtusum, S. papillosum, S. subsecundum). Constant species are Betula pubescens, Carex limosa, Equisetum luviaile, Menyanthes trifoliata, 230 231 Peucedanum palustre, Phragmites australis, Potenilla palustris, Vaccinium oxycoccos (Oxycoccus palustris). In hollows, there dominate Carex limosa, Rhynchospora alba, Sphagnum cuspidatum. Signiicant area is covered by eutrophic and mesotrophic communiies of Carex elata. Raised bogs occupy a small area. Main dominants are Eriophorum vaginatum and Sphagnum fallax. Constant species are Andromeda polifolia, Vaccinium oxycoccos and Pinus sylvestris. Pinus sylvestris woods are represented by dry lichen pine woods (dominants: Cladonia miis, Corynephorus canescens), woods dominated by Vaccinium myrillus and Pleurozium schreberi (constant species: Betula pendula, Frangula alnus, Melampyrum pratense, Molinia caerulea, Sorbus aucuparia, Vaccinium viis idaea), Sphagnum pine woods. Besides there are Betula pubescens and Alnus gluinosa woods with a layer of peat mosses. Botanical significance. The largest transiion mire in Ukraine. Criterion C • D2.3 Transition mires and quaking bogs; area: 8000 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Андрієнко Т.Л. ПЗ Рівненський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 313–324. 2. Андрієнко Т.Л., Балашов Л.С., Прядко О.І. Унікальний болотний масив Переброди на Ровенщині // Укр. ботан. журн. – 1976. – 33, № 5. – С. 532–536. 3. Андрієнко Т.Л., Прядко О.І., Онищенко В.А. Раритетна компонента флори Рівненського природного заповідника // Укр. ботан. журн. – 2006. – 63, № 2. – С. 220–228. 4. Онищенко В., Прядко О., Андрієнко Т. Рослинність ділянки Переброди Рівненського природного заповідника // Науковий вісник Східноєвропейського національного ун-ту ім. Лесі Українки. Сер. Біологічні науки. – 2015. – 13. – С. 32–49. 5. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Peresyp Aktaskoho Ozera dunes and sandy shores – 15.0%; B2 Coastal shingle – 10.0%; E1 Dry grasslands – 22.0%; E6 Salt steppes – 12.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 4.0%. Futher habitat description. A2.1 Litoral coarse sediment; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; B1.2 Sand beaches above the dritline; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; E1.1 Inland sand and rock with open vegetation; H5.6 Trampled areas. V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Пересип Актаського озера. Transliteraion/Translaion variants: Peresyp of Aktash Lake. Area: 189.0 ha. Altitude: 0–3 m. Latitude: 45°23’18” N (45.3884°). Longitude: 35°55’05” E (35.9181°). Administrative regions. Autonomous Republic of Crimea: Lenine raion; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 37.0%; B – 25.0%; E – 34.0%; H – 4.0%. Habitats. Level 2. A2 Littoral sediment – 4.0%; A5 Sublitoral sediment – 33.0%; B1 Coastal Land use: nature conservaion and research – minor, tourism/recreaion – minor. Protected areas: overlaps with state ornithological reserve “Astaninski Plavni” (“Ostaninski Zaplavy”). Threats: climate change/ sea level rise – low, development (recreaion/tourism) – medium. General description. A bar composed of sand and seashells. Vegetaion of the beach is formed by Leymus sabulosus, Crambe mariima, Сakile euxina, Centaurea odessana, Carex colchica, Eryngium maritimum. The most elevated places are dominated by Artemisia marschalliana, Sipa capillata, Ephedra distachya, Agropyron cimmericum. On the side opposite the sea, there are mesic and wet plant communiies dominated by Elytrigia elongata, Elyigia repens, Glycyrrhiza glabra, Limonium meyeri. Botanical significance. Important area for seaside threatened species Alyssum borzaeanum (Odontarrhena borzaeana) and Thymus litoralis. Criterion A • Agropyron cimmericum Nevski; A(i); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. 232 233 • Alyssum borzaeanum Nyár. (Odontarrhena borzaeana (Nyár.) D.A.German); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Thymus litoralis Klokov et Shost.; A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Create an Emerald Site including the enire IPA. Literature 1. Корженевский В.В., Волкова Т.А., Клюкин А.А. О синтаксономическом положении растительности пляжей и формирующихся дюн Азовского побережья Керченского полуострова // Ботан. журн. – 1984. – Т. 69, № 11. – С. 1462–1467. 2. Котова И.Н. Флора и растительность Керченского полуострова // Тр. Никит. ботан. сада. Материалы по флоре и растительности Крыма. – 1961. – Т. 35. – С. 64–168. 3. Новосад В.В. Флора Керченско-Таманского региона. – Киев: Наукова думка. – 1992. – 280 с. cretacea, Scrophularia cretacea, Silene supina, Teucrium polium. Steppe vegetaion is dominated by Sitpa capillata, Bromopsis riparia, Festuca valesiaca, Koeleria cristata, Poa angusifolia, Elytrigia repens. There occur steppes with dominance of shrubs (Caragana frutex, Chamaecyisus austriacus, Chamaecyisus ruthenicus). Typical species of the steppe vegetaion are also Adonis vernalis, Salvia nutans, Stachys recta, Linum flavum, Thalictrum minus. Shrub vegetaion is formed by Cerasus fruicosa, Crataegus sp., Prunus spinosa, Rosa sp. Petro-Ivanivka О.V. Bezrodnova Ukrainian name: Петро-Іванівка. Area: 188 ha. Altitude: 90-160 m. Latitude: 49°55’22” N (49.9226°). Longitude: 37°40’43”E (37.6785°). Administrative regions. Kharkiv region: Dvorichna raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 73.3%; F – 2.0%; G – 15.7%; H – 9.0%. Habitats. Level 2. E1 Dry grasslands – 72.7%; E5 Woodland fringes and clearings and tall forb stands – 0.6%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 15.7%; H2 Screes – 9.0% Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; forestry – minor. Protected areas: – Threats: abandonment/reducion of land management – low; extracion (minerals/ quarries) – low. General description. Slopes with outcrops of chalk and steppes. Dominants of vegetaion on chalk are Androsace koso-poljanskii, Artemisia hololeuca, Hyssopus cretaceus, Linum ucrainicum, Thymus calcareus. Other typical species are Asperula tephrocarpa, Astragalus albicaulis, Astragalus austriacus, Bupleurum falcatum, Carex humilis, Cephalaria uralensis, Euphorbia stepposa, E. seguierana, Gypsophila fasigiata, Hedysarum grandilorum, Mathiola fragrans, Odontites luteus, Onosma tanaiica, Pimpinella titanophila, Polygala 234 Botanical significance. Important area for conservaion of Androsace koso-poljanskii and other endemic species of chalk outcrops. Criterion A • Alyssum gymnopodum P.A.Smirn. (Odontarrhena gymnopoda (P.A.Smirn.) D.A.German); A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Androsace koso-poljanskii Ovcz.; A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. 235 Conservaional proposals: create a state botanical reserve and an Emerald Site. Literature 1. Безроднова О.В. Раритетные кальцефильные виды в Гербарии Харьковского национального университета имени В. Н. Каразина (CWU) // Вісник Харківського національного університету імені В.Н. Каразіна. Серія: біологія. – 2015. Вип.25. – С. 16-26. Pidlyska Hora V.A. Onyshchenko, T.D. Solomakha Ukrainian name: Підлиська гора. Transliteraion/Translaion variants: Pidlys’ka Gora, Pidlys’ka Hill. Area: 81.9 ha. Altitude: 262–374 m. Latitude: 49°55’56” N (49.9321°). 236 Longitude: 24°50’36” E (24.8432°). Administrative regions. Lviv region: Zolochiv raion. Ownership: state. Biogeographic regions: coninental Habitats. Level 1. E – 22.8%; F – 1.0%; G – 75.2%; H – 1.0% Habitats. Level 2. E1 Dry grasslands – 20.5%; E5 Woodland fringes and clearings and tall forb stands – 0.3%; E7 Sparsely wooded grasslands – 2.0%; F3 Temperate and mediterranean-montane scrub – 1.0%; G1 Broadleaved deciduous woodland – 8.0%; G3 Coniferous woodland – 17.0%; G4 Mixed deciduous and coniferous woodland – 20.2%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 30.0%; H3 Inland cliffs, rock pavements and outcrops – 0.5%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; E7.2 Sub-coninental parkland; F3.1 Temperate thickets and scrub; G1.6 Fagus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.F Highly artificial coniferous plantations; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H3.2 Basic and ultrabasic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: nature conservation and research – major, forestry – major. Protected areas: included in regional nature monument “Pidlyska Hora abo Hora Markiana Shashkevycha”. Threats: abandonment/reducion of land management – medium, burning of vegetaion – low. General description. A hill with the forest, grassland and limestone outcrops. The grassland vegetaion is dominated by Briza media, Carex lava, Carex humilis, Dactylis glomerata, Festuca pratensis, Festuca rubra, Festuca rupicola, Inula ensifolia, Teucrium chamaedrys. Frequent species are Allium lusitanicum s.l. (Allium montanum auct.), Anemone sylvestris, Asperula cynanchica, Bupleurum falcatum, Campanula sibirica, Centaurea pannonica, Euphorbia cyparissias, Galium verum, Lembotropis nigricans, Leontodon hispidus, Linum catharicum, Onobrychis arenaria, Pimpinella saxifraga, Plantago media, Potenilla incana, Primula veris, Prunella grandilora, Ranunculus polyanthemos, Ranunculus zapalowiczii, Scabiosa ochroleuca, Thymus marschallianus, Thymus pannonicus, Salvia pratensis. Botanical significance. Important area for Carlina onopordifolia and Cypripedium calceolus. Criterion A • Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł.; A(i), A(ii), A(iv); abundance: frequent (289 individuals); trend: stable; species data quality: good; trend data quality: medium. • Cypripedium calceolus; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals: do not allow aforestaion. Literature 1. Дідух Я., Коротченко І. Ксеротермна рослинність північно-західного Поділля // Вісник Львівського ун-ту. Серія біологічна. – 2003. – 34. – С. 82–91. 2. Мельник В.І., Скоропляс І.О., Баточенко В.М. Сучасний стан популяцій Carlina onopordifolia (Asteraceae) на західному Волино-Поділлі // Укр. ботан. журн. – 2014. – 71, № 2. – С. 35–48. 3. Мельник В.И., Скоропляс И.О. Современное состояние популяций Сarlina onopordifolia Besser ex Szafer, Kulcz. & Pawl. в Украине // Austrian Journal of Technical and Natural Sciences. – 2014. № 9–10. – С. 21–24. 237 4. Скоропляс І.О. Географічне поширення Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł. (Asteraceae) в Україні // Ботанічні дослідження – 2014: Збірник наукових праць V Всеукраїнської науково-практичної конференції молодих учених і студентів. – Житомир: Вид-во ЖДУ ім. І. Франка, 2014. – С. 430–434. Podvirivka I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Подвір’ївка. Area: 45.4 ha. Altitude: 172-221 m. Latitude: 48°20’36” N (48.3432°). Longitude: 26°48’29” E (26.8079°). Administraive regions: Chernivtsi region: Kelmentsi raion. Landuse: agriculture (animals) – major. Protected areas: –. Threats: agricultural intensiicaion/expansion (grazing) – low. General description. Slopes with grasslands dominated by Briza media, Dactylis glomerata, Elytrigia intermedia, Festuca pratensis, F. valesiaca, Helictotrichon pubescens, Koeleria cristata, Poa pratensis. Other frequent species are Achillea millefolium, Carex tomentosa, Centaurea jacea, Filipendula vulgaris, Galium verum, Knautia arvensis, Leontodon hispidus, Primula veris, Ranunculus polyanthemos, Salvia pratensis, Serratula lycopifolia, Vicia tetrasperma. The synusium of spring ephemeroids consists of Friillaria montana, Ficaria stepporum, Bulbocodium versicolor. Botanical significance. Important populaions of Serratula lycopifolia and Friillaria montana. Criterion A • Fritillaria montana Hoppe; А (ii); abundance: occasional; trend: stable; species data quality: good; trend data quality: medium. • Serratula lycopifolia (Vill.) A. Kern.; А (ii); abundance: occasional; trend: stable; species data quality: good; trend data quality: medium. Conservaion proposals. Create a state botanical reserve and an Emerald Site. Literature 1. Каземірська М.А., Токарюк А.І., Чорней І.І. Насіннєва продуктивність Fritillaria montana Hoppe (Liliaceae) в популяціях на північно-східній межі ареалу (середнє ПрутДністров’я) // Заповідна справа в Україні. – 2010. – Т. 16, Вип. 2. – С. 9–14. 2. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. Pohorylivka Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 97.0%; F – 2.0%; G – 1.0%. Habitats. Level 2. E1 Dry grasslands – 88.0%; E2 Mesic grasslands – 10.0%; E7 Sparsely wooded grasslands – 1.0%; F3 Temperate and mediterranean-montane scrubs – 2.0%; G1 Broadleaved deciduous woodland – 1.0%. Futherhabitat description: E1.2 Perennial calcareous grassland and basic steppes; E7.2 Sub-continental parkland. I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Погорилівка. Area: 94.7 ha. Altitude: 194-258 m. Latitude: 48°32’26” N (48.5406°). Longitude: 25°59’18” E (25.9883°). Administraive regions: Chernivtsi region: Zastavna raion. Ownership: state (major), municipal. Biogeographic regions: coninental. Habitats. Level 1. E – 96.7%; F – 2.0%; H – 0.6%; J – 0.7% Habitats. Level 2. E1 Dry grasslands – 96.7%; F3 Temperate and mediterranean-montane scrubs – 2.0%; H1 Terrestrial underground caves, cave systems, passages and waterbodies; H3 Inland cliffs, rock pavements and outcrops – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%; J3 Extractive industrial sites – 0.7%. Futherhabitat description: E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; H3.5 Almost bare rock pavements, including limestone pavements; H5.6 Trampled areas. Landuse: agriculture (animals) – minor; nature conservaion and research – major. Protected areas: includes Chornopototskyi state karst-spelaean reserve (49 ha), Martynivske regional nature preserve (zapovidne urochyshche) (26 ha), Pechera Fushteika regional 238 239 geological nature monument (2.5 ha). Threats: agricultural intensiicaion/expansion (grazing) – low. General description. Karst area with grasslands and gypsum outcrops. Grasslands are dominated by Carex humilis, Carex montana, Festuca valesiaca, Koeleria cristata, Stipa Literature 1. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. 2. Чорней І.І., Скільський І.В., Коржик В.П., Буджак В.В. Заповідні об’єкти Буковини загальнодержавного значення як основа регіональної екологічної мережі // Заповідна справа в Україні. – 2001. – Т. 7, вип. 2. – С. 73–98. 3. Чорней І.І., Токарюк А.І., Буджак В.В., Скільський І.В. Заповідні урочища Північної Буковини та Хотинщини: загальний огляд, раритетні флора і фауна // Заповідна справа в Україні. – 2009. – Т. 15, вип. 1. – С. 82–100. Polonskyi Lis V.A. Onyshchenko Ukrainian name: Полонський ліс. Transliteraion/Translaion variants: Polons’kyi Forest. Area: 1704.0 ha. Altitude: 236–246 m. Latitude: 50°09’57” N (50.1659°). Longitude: 27°24’44” E (27.4122°). Administrative regions. Khmelnytskyi region: Polonne raion, Shepeivka raion. Ownership: state. capillata, Stipa pennata, Inula ensifolia, Molinia caerulea agg. There are Adonis vernalis, Aconitum anthora, Asperula cynanchica, Astragalus austriacus, A. onobrychis, Anthericum ramosum, Chamaecytisus albus, Filipendula vulgaris, Galium verum, Gypsophila thyraica, Inula ensifolia, Iris hungarica, Potentilla arenaria, Pulsailla grandis, Pulsailla patens, Pulsatilla pratensis, Salvia pratensis, S. verticillata, Securigera varia, Teucrium chamaedrys, T. pannonicum, Thymus marschallianus, Trifolium montanum. Botanical significance. One of the largest areas of dry grasslands in western Ukraine. There are many protected species including Cypripedium calceolus, Iris hungarica, Gypsophila thyraica, Pulsailla grandis, Pulsailla patens, Pulsailla pratensis, Sipa pennata. Criterion A • Gypsophila thyraica A.Krasnova; A(iiі); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Iris hungarica Waldst. & Kit.; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. • Pulsailla grandis Wend.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 80 ha; trend: stable; area data quality: medium; trend data quality: medium. 240 241 Biogeographic regions: coninental. Habitats. Level 1. C – 2.6%; D – 2.0%; E – 0.1%; G – 94.3%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.6%; C2 Surface running waters – 0.0%; C3 Littoral zone of inland surface waterbodies – 2.0%; D5 Sedge and reedbeds, normally without free-standing water – 2.0%; E3 Seasonally wet and wet grasslands – 0.1%; G1 Broadleaved deciduous woodland – 73.3%; G3 Coniferous woodland – 10.0%; G4 Mixed deciduous and coniferous woodland – 11.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – major; tourism/recreaion – minor. Protected areas: included in Maliovanka regional landscape park, included in Emerald Site “Maliovanka Regional Landscape Park”. Threats: forestry (intensiied forest management) – low. General description. Major vegetaion type is the mesotrophic moist forests dominated by Quercus robur in the tree layer and Carex brizoides in the herb layer. Usually there is the shrub layer with prevailng of Frangula alnus. Other species of signiicant constancy are Betula pendula, Calamagrosis arundinacea, Corylus avellana, Lysimachia vulgaris, Maianthemum bifolium, Pinus sylvestris, Populus tremula. Other forest types: Quercus robur forests dominated by Convallaria majalis or Pteridium aquilinum with presence of Betonica oicinalis, Serratula inctoria; Pinus sylvestris and mixed Pinus sylvestris – Quercus robur forests dominated by Vaccinium myrillus and Pleurozium shreberi; Alnus gluinosa forests and swamps. Botanical significance. Important for conservaion of acidophilous oak forests. Criterion C • G1.8 Acidophilous Quercus-dominated woodland; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Create a state botanical reserve. Do not allow clearcuing. Literature 1. Природа ункального краю – Малого Полісся / Т.Л. Андрієнко, Л.С. Юглічек, Р.Г. Білик, О.І. Прядко, М.Д. Матвєєв, Л.П. Казімірова, В.А. Онищенко, Л.Г.Безусько, Р.Я. Арап, М.О. Тарасенко / під ред. Т.Л.Андрієнко. – Кам’янець-Подільський: Вид-во ПП Мошинського В.С., 2010. – 254 с. Polonyna Borzhava V.A. Onyshchenko Ukrainian name: Полонина Боржава. Area: 4448.0 ha. Altitude: 1100–1682 m. Latitude: 48°38’46” N (48.6460°). Longitude: 23°13’59” E (23.2332°). Administrative regions. Zakarpatska region: Mizhhirya raion, Svaliava raion, Volovets raion. Ownership: state, private. Biogeographic regions: alpine. Habitats. Level 1. E – 50.6%; F – 45.2%; G – 3.7%; H – 0.5%. Habitats. Level 2. E1 Dry grasslands – 44.0%; E4 Alpine and subalpine grasslands stands – 6.3%; E5 Woodland fringes and clearings and tall forb stands – 0.3%; F2 Arctic, alpine and subalpine scrub – 1.6%; F4 Temperate shrub heathland – 43.6; G1 Broadleaved deciduous woodland – 3.7%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. E1.7 Non-Mediterranean dry acid and neutral closed grassland; E4.1 Vegetated snow-patch; E4.2 Moss and lichen dominated mountain summits, ridges 242 243 and exposed slopes; E4.3 Acid alpine and subalpine grassland; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F4.2 Dry heaths; G1.6 Fagus woodland; H3.1 Acid silicious inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – major. Protected areas: same as Emerald Site “Polonyna Borzhava”. Threats: abandonment/reducion of land management – low. General description. Grasslands and heaths above the upper limit of the forest. Main dominant species are Nardus stricta and Vaccinium myrillus. Botanical significance. Important area for heaths and mountain grasslands. Criterion C • E1.71 Nardus stricta swards; area: 1400 ha; trend: stable; area data quality: medium; trend data quality: poor. • E4.11 Boreo-alpine acidocline snow-patch grassland and herb habitats; area: 1 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.3 Acid alpine and subalpine grassland; area: 220 ha; trend: stable; area data quality: medium; trend data quality: poor. • F4.2 Dry heaths; area: 1800 ha; trend: stable; area data quality: medium; trend data quality: poor. Conservaion proposals. Create a naional protected area. Literature 1.Малиновський К.А., Крічфалушій В.В. Рослинні угруповання високогір’я Українських Карпат. – Ужгород, 2002. – 244 с. Polovetskyi Step V.P. Kolomiychuk Ukrainian name: Половецький степ. Transliteraion/Translaion variants: Polovtsian Steppe. Area: 2120.0 ha. Altitude: 59–135 m. Latitude: 47°10’47” N (47.1795°). Longitude: 36°52’26” E (36.8739°). Administrative regions. Donetsk region: Volodarske raion; Zaporizhia region: Berdiansk raion, Bilmak raion. Ownership: state, private. Biogeographic regions: steppic. Habitats. Level 1. C – 1.2%; D – 0.9%; E – 91.7%; F – 1.0%; G – 4.2%; H –1.0%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C2 Surface running waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 1.0%; D5 Sedge and reedbeds, normally without free-standing water – 0.9%; E1 Dry grasslands – 90.6%; E2 Mesic grasslands – 1.0%; E5 Woodland fringes and clearings and tall forb stands – 0.1% F3 Temperate and mediterranean-montane scrub – 1.0%; G1 Broadleaved deciduous woodland – 4.0%; G3 Coniferous woodland – 0.2%; H3 Inland cliffs, rock pavements and outcrops – <0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; F3.1 244 Temperate thickets and scrub; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.3 Mediterranean riparian woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations; H3.2 Basic and ultra-basic inland cliffs; H5.6 Trampled areas. Land use: agriculture (animals) – major, mowing/hay making – minor, nature conservation and research – 47%. Protected areas: overlaps (about 990 ha) with Meotyda naional nature park and Emerald Site “Meotyda”. Threats: abandonment/reducion of land management – low; agricultural intensiicaion/ expansion (grazing) – low, forestry (aforestaion) – medium. General descripion. Valleys of the Berda river in its middle reaches and the Karaiuk river with the gulches lowing in them. Major habitat type is the steppe. Dominant species are Festuca valesiaca, Sipa capillata, S. lessingiana, S. ucrainica, Koeleria cristata, in some places Sipa pulcherrima. Other constant species are Adonis vernalis, Asrtagalus onobrychis, A. palescens, Euphorbia stepposa, Jurinea arachnoidea, Haplophyllum suaveolens, Onobrychis tanaiica, Oxytropis pilosa, Phlomoides tuberosa (Phlomis tuberosa), Plantago stepposa, Pulsailla pratensis, Stachys transsilvanica, Thymus marschallianus. In more mesic habitats, rhizomatous grasses Poa angusifolia, Elytrigia repens, Alopecurus pratensis dominate. In some places there are shrub steppes with co-dominance of Caragana frutex, Amygdalus nana. Typical species of the steppes on stony soils are Festuca valesiaca, Achillea leptophylla, Helicrysum arenarium, Thymus dimorphus. Besides there are riverine forests of Salix alba, Populus alba, P. nigra, plantaions of Robinia pseudoacacia, Pinus pallasiana, Ulmus minor, Fraxinus lanceolata, shrub communiies with dominance of Prunus spinosa, Rhamnus catharica, Crataegus fallacina, saline medows with dominance of Festuca regeliana and Elytrigia elongata, beds of Phragmites australis, granite outcrops. 245 Botanical significance. Well-preserved coninental steppe. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1900 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Сreate a state botanical reserve. Literature 1. Вакаренко Л.П., Мовчан Я.І., Турута О.Є. Рослинні раритети середньої течії р. Берди // Укр. ботан. журн. – 1996. – 53, № 5. – С. 598–603 2. Вакаренко Л.П., Мосякін С.Л., Генов А.П. Наукове обгрунтування необхідності створення міжрегіонального ландшафтного парку “Надбердянський степ” (Північне Приазов’я) // Заповідна справа в Україні. – 2000. – Т. 6. – С. 17–27. 3. Ландшафты, растительный покров и животный мир регионального ландшафтного парка “Меотида” / Г. Н. Молодан, С. А. Приходько, С. В. Третьяков и др. – Донецк: Ноулидж, 2010. – 184 с. europaea), Vaccinium myrillus (dom.), Vaccinium viis-idaea. In termophilous Quercus robur forests, Convallaria majalis dominates. Other frequent species are Allium lusitanicum s.l. (Allium montanum auct.), Campanula persicifolia, Centaurea phrygia, Fragaria vesca, Lathyrus niger, Meliis sarmaica, Polygonatum odoratum, Potenilla alba, Pteridium aquilinum, Serratula inctoria, Vicia cassubica. Botanical significance. Large populaion of Dracocephalum ruyschiana. One of the best species-rich oak woods in the northen Ukraine. Criterion A Potashnianski Lisy O.O. Orlov, V.A. Onyshchenko Ukrainian name: Поташнянські ліси. Transliteraion/Translaion variants: Potashnia Forests. Area: 852.0 ha. Altitude: 174–190 m. Latitude: 50°25'32" N (50.4253°). Longitude: 29°18'56" E (29.3154°). Administrative regions. Zhytomyr region: Radomyshl raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 1.0%; G – 98.0%; H – 1.0%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 29.9%; G3 Coniferous woodland – 29.9%; G4 Mixed deciduous and coniferous woodland – 29.8%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 8.4%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. G1.7 Thermophilous deciduous woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – 46%. Protected areas: includes Bervy regional botanical reserve (392 ha). Threats: forestry (intensiied forest management) – medium. General description. Vegetaion is represented mainly by forests (deciduous, mixed and coniferous approximately in equal parts). Constatnt species of drier Pinus sylvestris forests are Сhamaecyisus zingeri, Campanula rotundifolia, Melampyrum pratense, Hieracium umbellatum, Peucedanum cervaria (dom.), Solidago virgaurea, Pleurozium schreberi (dom.), Dicranum polysetum (dom.). In weter pine forests, constant species are Frangula alnus (dom.), Sorbus aucuparia, Dryopteris carthusiana, Luzula pilosa, Melampyrum pratense, Mollinia caerulea (dom.), Pteridium aquilinum (dom.), Trientalis europaea (Lysimachia 246 • Dracocephalum ruyschiana L.; A(ii); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • G1.7 Thermophilous deciduous woodland; area: 150 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Якушенко Д.М., Вініченко Т.С. Еколого-ценотична характеристика Dracocephalum ruyschiana L. на південному сході Житомирського Полісся // Вісник Київського національного університету імені Тараса Шевченка. Інтродукція та збереження рослинного різноманіття. – 2005. – Вип. 8. – С. 42–44. 247 Probabyn I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Пробабин. Area: 4.6 ha. Altitude: 260–287 m. Latitude: 48°39'39" N (48.6609°). Longitude: 25°35'14" E (25.5872°). valesiaca, Koeleria cristata, Poa angustifolia. Other frequent species: Adonis vernalis, Asperula cynanchica, Astragalus austriacus, Cephalaria uralensis, Chamaecytisus podolicus, Filipendula vulgaris, Fragaria viridis, Gypsophila thyraica, Hyacinthella leucophaea, Inula ensifolia, Muscari botryoides, Potentilla arenaria, Salvia pratensis, Securigera varia, Teucrium chamaedrys, Thymus marschallianus, Trifolium montanum. Botanical significance. Important area for endemic species Aconitum pseudanthora, Chamaecytisus podolicus, Gypsophila thyraica; locus classicus of Chamaecyisus podolicus. There are other Crierion A species: Iris hungarica, Pulsailla grandis, Pulsailla patens. Criterion A • Aconitum pseudanthora Błocki ex Pacz. A(iii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Chamaecytisus podolicus (Błocki) Klásk. A(iv); abundance: frequent; trend: unknown; species data quality: good; trend data quality: medium. • Gypsophila thyraica A.Krasnova A(iiі); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Create a state botanical nature monument. Provalskyi Step Ukrainian name: Провальський степ. Transliteraion/Translaion variants: Proval'skyi Steppe. Area: 587.5 ha. Altitude: 115–231 m. Latitude: 48°07'55" N (48.1319°). Administrative regions. Ivano-Frankivsk region: Horodenka raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1: E – 98.0%, F – 2.0%. Habitats. Level 2: E1 Dry grasslands – 98.0%, F3 Temperate and mediterranean-montane scrub – 2.0%. Futher habitat description: E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub. Land use: agriculture (animals) – minor. Protected areas: –. Threats: agricultural intensiicaion/expansion (grazing) – low, extracion (mineral/quarries) – low. General description. Grasslands dominated by Carex humilis, Festuca rupicola, Festuca 248 249 V.A. Onyshchenko Longitude: 39°49'09" E (39.8191°). Administrative regions. Luhansk region: Dovzhansk (Sverdlovsk) raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 77.0%; D – 1.0%; F – 1.0%; G – 20.0%; H – 1.0%. Habitats. Level 2. E1 Dry grasslands – 76.0%; E2 Mesic grasslands – 1.0%; D5 Sedge and reedbeds, normally without free-standing water – 1.0%; F3 Temperate and mediterraneanmontane scrub – 1.0%; G1 Broadleaved deciduous woodland – 20.0%; H2 Screes – 0.1%; H3 Inland cliffs, rock pavements and outcrops – 0.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without freestanding water; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; H5.3 Sparsely- or unvegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservaion and research – 100%. Protected areas: included in Luhanskyi nature reserve (same as division Provalskyi Step of the reserve), included in Emerald Site "Luhanskyi Nature Reserve". Threats: abandonment/reducion of land management – low. General description. Major vegetaion of the area is steppe. Most common are steppes dominated by Sipa irsa. They are rich in mesic species: Anemone sylvestris, Filipendula vulgaris, Fragaria viridis, Inula hirta, Melampyrum argyrocomum, Trifolium alpestre, Trifolium montanum, Myosois popovii. A large area is occupied by the steppes of Sipa dasyphylla with signiicant admixture of Festuca rupicola, Festuca valesiaca, Elytrigia intermedia, Bromopsis riparia, Sipa capillata, Caragana frutex, Spiraea hypericifolia. On eroded soils, a typical dominant is Sipa ucrainica. On shallow gravel soils, there dominates Sipa pulcherrima, Sipa asperella, Sipa ucrainica, Botriochloa ischaemum with presence of Artemisia marschalliana, Cota inctoria (Anthemis inctoria), Ephedra distachya, Festuca valesiaca, Jurinea arachnoidea, Galatella villosa, Pimpinella itanophila, Psephellus marschallianus (Centaurea marschalliana), Salvia nutans, Tanacetum millefoliom, Teucrium polium, Thymus dimorphus. On northern slopes and in depressions, a large area is occupied by the grasslands with dominance of rhizomatous grasses Bromopsis riparia, Bromopsis inermis, Elytrigia intermedia, Poa angusifolia, Calamagrosis epigeios, Hierochloe repens with admixture of Galium verum, Inula hirta, Salvia nutans, Salvia tesquicola, Securigera varia, Phlomis pungens, Phlomoides tuberosa (Phlomis tuberosa), Trifolium alpestre, Trifolium montanum, Trifolium pratense. Halophyic steppes dominated by Festuca valesiaca and Galatella dracunculoides occur between ridges, their typical species are Artemisia santonica, Halimione verrucifera, Kochia prostrata, Limonium bungei, Pimpinella itanophila, Plantago tenuilora. On outcrops, there is open vegetaion with prevailing Thymus calcareus, Pimpinella itanophila, Artemisia marschalliana, Agropyron pecinatum. Typical species of these communiies are Spiraea hypericifolia, Spiraea crenata, Alyssum tortuosum (Odontarrhena tortuosa), Asperula tephrocarpa, Silene supina, Thymus dimorphus, Tulipa ophiophylla. Forests are dominated by Quercus robur, Fraxinus excelsior, Acer campestre; Acer tataricum, Rhamnus catharica, Sambucus nigra, Crataegus fallacina, Ligustrum vulgare, Euonymus verrucosus, Euonymus czernjaevii, Swida sanguinea (Cornus sanguinea); Aegopodium podagraria, Ficaria verna, Anemone ranunculoides, Scilla siberica, Corydalis solida, Corydalis marschalliana, Viola odorata, Melica picta, Poa nemoralis. The IPA consists of two clusters located at a distance of 4 km from each other. Botanical significance. Important area for conservaion of steppes. Criterion A • Delphinium sergii Wissjul.; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Onosma graniicola Klokov; A(iv); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 446 ha; trend: stable; area data quality: good; trend data quality: good. Literature 1. Біорізноманітність Луганського природного заповідника НАН України / сост. Т. Сова. – Луганськ: ЛГСІ, 2005. – 218 с. 2. Биоразнообразие Луганского природного заповедника: растительный мир / Составители: Сова Т. В., Русина Н. В., Гузь Г. В., Боровик Л. П., Шиян-Глотова А. В. – Луганск: Элтон–2, 2009. – 130 с. 3. Білик Г.І., Ткаченко В.С. Рослинний покрив Провальского степу // Укр. ботан. журн. – 1971. – 28, № 4. – С. 443–448. 4. Вєтрова З.І. Розподіл Евгленофітових у водоймах заповідника "Провальский степ" // Укр. ботан. журн. – 1988. – 45, № 4. – С. 58–61. 5. Кондратюк Е.Н., Бурда Р.И., Чуприна Т.Т., Хомяков М.Т. Луганский гocударственный заповедник. Растительный мир. – Киев: Наук. думка, 1988. – 188 с. 6. Маслова В.Р. Ліхенофлора Провальского степу // Зб. наук. праць "Інтродукція і акліматизація рослин на Україні". – 1979. – Вип. 15. – С. 51–54. 7. Надеина О.В. Лишайники Провальской степи (Украина) // Ботан. журн. – 2008. – 93, № 1. – С. 3–9. 8. Приходькова Л.П. Синьозелені водорості в грунтах заповідника "Провальський степ" // Укр. ботан. журн. – 1988. – 45, № 2. – С. 9–13. 9. Русіна Н.В. Історія та сучасний стан дослідження ліхенобіоти Луганського природного заповідника // Наукові праці Луганського природного заповідника. Рослинний і тваринний світ та його охорона. – Луганськ. – 2011. – Вип. 2. – С. 47–53 10. Сова Т.В., Боровик Л.П. ПЗ Луганський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 221–253. 11. Ткаченко В.С. Прогноз змін рослинності заповідника "Провальский степ" // Укр. ботан. журн. – 1981. – 38, № 1. – С. 83–89. 12. Ткаченко В.С. Темпи демутації та коригування прогнозу розпитку степової рослинності Провальского степу // Укр. ботан. журн. – 1990. – 47, № 2. – С. 49–54. 13. Ткаченко В.С., Чуприна Т.Т., Бакланов О.В. Заповідник Провальський степ (сучасний стан і завдання наукових досліджень) // Укр. ботан. журн. – 1979. – 36, № 4. – С. 352–356. 14. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 250 251 Riznykivka Ukrainian name: Різниківка. Area: 330.0 ha. Altitude: 100–160 m. Latitude: 48°50'22" N (48.8393°). Longitude: 38°01'40" E (38.0278°). Administrative regions. Donetsk region: Bakhmut (Artemivsk) raion. Ownership: state. Biogeographic regions: steppic. V.A. Onyshchenko quarries) – low, forestry (aforestaion) – medium. General description. Slope of the Riznykivska valley. The steppe vegetaion is dominated by Festuca valesiaca, Sipa capillata, S. lessingiana, S. pennata, S. tirsa, S. ucrainica. Dominants of the chalk outcrops are Artemisia hololeuca, Hyssopys cretaceus, Thymus cretaceus. Botanical significance. Important area for some endemic species of chalk outcrops. Criterion A • Linaria cretacea Fisch. ex Spreng.; A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Silene cretacea Fisch. ex Spreng.; A(ii), A(iv); abundance: occasional; trend: unknown; species data quality: poor; trend data quality: poor. Conservaion proposals. Create a state botanical reserve. Literature 1. Остапко В.М., Мулєнкова О.Г., Приходько С.А. Перспективні ботанічні об'єкти для включення до природно-заповідного фонду Донецької області та формування регіональної екомережі // Промышленная ботаника. Сборник научных трудов. – Донецк: Донецкий ботанический сад НАН Украины. – 2013. – Вып. 13. – С. 25–34 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Romosh Habitats. Level 1. E – 79.6%; F – 2.0%; G – 8.4%; H – 10.0%. Habitats. Level 2. E1 Dry grasslands – 79.6%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 7.7%; G3 Coniferous woodland – 0.7%; H2 Screes – 10.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; forestry – major. Protected areas: overlaps (about 320.0 ha) with regional botanical reserve "Kreidiana roslynnist bilia sela Kirove", included in Emerald Site "Riznykivskyi". Threats: agricultural intensiicaion/expansion (grazing) – low, extracion (minerals/ V.V. Datsiuk, V.A. Onyshchenko Ukrainian name: Ромош. Area: 636 ha. Altitude: 205–235 m. Latitude: 50°35'12" N (50.5867°). Longitude: 24°21'12" E (24.3533°). Administrative regions. Lviv region: Sokal raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1: E – 1.2%, G – 97.8%, H – 1.0% . Habitats. Level 2: E2 Mesic grasslands – 1.2%; G1 Broadleaved deciduous woodland – 69.8%; G3 Coniferous woodland – 14.0%; G4 Mixed deciduous and coniferous woodland – 14.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description: G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.F Highly artificial coniferous plantations; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H5.6 Trampled areas. Land use: forestry – major. Protected areas: –. Threats: abandonment/reducion of land management – low; forestry (intensiied forest management) – low. General description. The major vegetaion type is deciduous forests dominated by Quercus robur, Carpinus betulus, Betula pendula. Dominants of the herb layer are Convallaria majalis, Galium odoratum, Stellaria holostea, Asarum europaeum. Frequent species are Betula 252 253 pendula, Fragaria vesca, Frangula alnus, Maianthemum bifolium, Pulmonaria obscura, Sanicula europaea, Sorbus aucuparia, Viola mirabilis. Besides there are plantaions of Pinus sylvestris with dominance of Pleurozium schreberi in the moss later. Botanical significance. One of the largest populaions of Cypripedium calceolus in Ukraine. The density of populaion is the highest in Pinus sylvestris wood in a former quarry of chalk (219 individuald per 0.3 ha in the early 1980th). Typical density is 5–50 individuals per ha. Cypripedium calceolus is present both in deciduous and coniferous forests. Criterion A • Cypripedium calceolus; A(ii); abundance: frequent; trend: decreasing; species data quality: good; trend data quality: medium. Conservaion proposals. Create a state botanical reserve. Literature 1. Вавриш П.О., Собко В.Г. Рідкісна популяція Cypripedium calceolus L. на Волинській височині // Укр. ботан. журн. – 1984. – 41, № 2. – С. 86–88. 2. Мельник В.І., Логвиненко І.П. Поширення та сучасний стан популяцій Cypripedium calceolus L. (Orchidaceae) на Волинській височині // Укр. ботан. журн. – 2013. – 70, № 6. – С. 788–791. 3. Собко В.Г. Орхідеї України. – Київ: Наук. думка, 1989. – С. 191 с. 254 Rys Ukrainian name: Рись. Area: 320.5 ha. Altitude: 175–192 m. Latitude: 51°15'42" N (51.26156°). Longitude: 25°22'59" E (25.38314°). Administrative regions. Volynska region: Manevychi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. G – 99.0%; H – 1.0%. V.A. Onyshchenko Habitats. Level 2. G1 Broadleaved deciduous woodland – 10.0%; G3 Coniferous woodland – 49.0%; G4 Mixed deciduous and coniferous woodland – 40.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion. G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.1 Abies and Picea woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; H5.6 Trampled areas. Land use: forestry – minor, nature conservation and research – minor. Protected areas: same as Rys state zoological reserve, included in Emerald Site "Cherevaskyi Lis". Threats: forestry (intensiied forest management) – low. General description. Forest dominated by Pinus sylvestris, Betula pendula, Alnus gluinosa, Picea abies. 255 Botanical significance. One of the largest locaions of Picea abies forests in the latland part of Ukraine. Criterion C • G3.1F Enclave Picea abies forests; area: 100 ha; trend: stable; area data quality: poor; trend data quality: poor. Conservaion proposals. Do not allow clearcuings. Create an Emerald Site including the enire IPA. Samarskyi Lis V.A. Onyshchenko Ukrainian name: Самарський ліс. Transliteraion/Translaion variants: Samara Forest, River Samara Forest. Area: 14372.0 ha. Altitude: 51–110 m. Latitude: 48°42'27" N (48.7075°). Longitude: 35°31'50" E (35.5306°). Administrative regions. Dnipropetrovsk region: Novomoskovsk raion, Pavlohrad raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 3.8%; D – 1.5%; E – 17.4%; F – 0.1%; G – 76.7%; H – 0.5%. Habitats. Level 2. C1 Surface standing waters – 1.4%; C2 Surface running waters – 1.9%; C3 Littoral zone of inland surface waterbodies – 0.5%; D5 Sedge and reedbeds, normally without free-standing water – 1.2%; D6 Inland saline and brackish marshes and reedbeds – 0.1%; E1 Dry grasslands – 0.2%; E2 Low and medium alitude hay meadows – 15.1%; E3 Seasonally wet and wet grasslands – 1.0%; E6 Inland salt steppes – 1.3%; F9 Riverine and 256 fen scrubs – 0.1%; G1 Broadleaved deciduous woodland – 41.4% G3 Coniferous woodland – 31.7%; G4 Mixed deciduous and coniferous woodland – 3.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat descripion. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-idal, smooth-lowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; D6.1 Inland saltmarshes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; E6.2 Coninental inland salt steppes; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian loodplain and gallery woodland; G1.3 Mediterranean riparian woodland; G1.B Non-riverine Alnus woodland; G3.F Highly ariicial coniferous plantaions; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G4.C Mixed Pinus sylvestris – thermophilous Quercus woodland; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: forestry – 80%; mowing/hay making – 10%; tourism/recreaion – minor. Protected areas: includes state ornithological reserve "Bulakhivskyi lyman" (100 ha), regional ornithological reserve "Vasylivska kolonia sirykh chapel" (144 ha), botanical nature monument "Dilianka nasadzhen sosny zvychainoi" (43 ha), regional botanical nature monument "Vysokoproduktyvni nasadzhennia sosny zvychainoi" (5 ha), regional botanical nature monument "Dilianka vikovych dubiv Vasylivskoi dachi" (3.4 ha), regional botanical nature monument "Shtuchni dubovi nasadzhennia" (4.3 ha), regional botanical nature monument "Shtuchni dubovi nasadzhennia" (2.2 ha), regional botanical nature monument "Storichni dubovi nasadzhennia pryrodnoho pokhodzhennia" (7.0 ha), regional botanical nature monument "Storichni dubovi nasadzhennia pryrodnoho pokhodzhennia" (1.9 ha), regional botanical nature monument "Stolitni dubovi nasadzhennia" (1.8 ha), overlaps (13136 ha) with Emerald Site "Samarskyi Lis". Threats: agricultural intensiicaion/expansion (arable) – low; development (recreaion/ tourism) – low; forestry (intensiied forest management) – medium. General descripion. The valley of the Samara river with broadleaved forests and meadows in the loodplain and pine forests on the sand terrace. The tree layer of the broadleaved forests is dominated by Quercus robur (major), Fraxinus excelsior, Tilia cordata, Ulmus laevis, Ulmus minor. In other layers, there prevail Acer tataricum, Aegopodium podagraria, Aristolochia clemaiis, Calamagrosis epigeios, Convallaria majalis, Frangula alnus, Glechoma hederacea, Rubus caesius, Stellaria holostea, Urica dioica. Species of signiicant constancy are also Anthriscus sylvestris, Asarum europaeum, Geum urbanum, Polygonatum mulilorum, Pulmonaria obscura, Viola hirta, Viola mirabilis. Interesing are saline broadleaved woods with presence of Carex melanostachya, Limonium gmelinii, Peucedanum laifolium, Silaum silaus. Oak forest is also on the slope of the right bank of the Samara river. Another important forest types are Alnus gluinosa swamp and Populus nigra wood, oten co-dominated by Populus alba, Salix alba or Salix fragilis. The tree layer of pine forests consists of Pinus sylvestris with paricipaion of Betula pendula, Quercus robur and Populus tremula. The pine forest occupies soils of diferent moister: dry (with Festuca beckeri, Koeleria sabuletorum, Sempervivum ruthenicum, Thymus pallasianus, Cladonia foliacea, Cladonia furcata, Cladonia rangiferina), mesic (with Anthericum ramosum, Calamagrosis epigeios (main dominant), Dianthus campestris, Hypericum perforatum, Melampyrum pratense, Peucedanum oreoselinum, Solidago virgaurea, Pleurozium schreberi, Dicranum polysetum), 257 moist (with Molinia caerulea), wet (with Calamagrosis canescens). In depressions on the sand terrace, among pine forest, there are Betula pubescens woods with the Sphagnum layer and wet Populus tremula woods. On dry sand, there are grasslands dominated by Festuca beckeri, Sipa borysthenica with presence of Artemisia marschalliana, Euphorbia seguieriana, Koeleria sabuletorum. Floodplain meadows are dominated by Bromopsis inermis, Calamagrosis epigeios, Elytrigia repens, Festuca pratensis with presence of Achillea millefolium, Carex praecox, Centaurea scabiosa, Convolvulus arvensis, Euphorbia seguieriana, Euphorbia virgata, Galium verum, Gypsophila paniculata, Lathyrus tuberosus, Lotus ucrainicus, Poa angusifolia, Poa pratensis, Securigera varia, Vicia cracca. In weter habitats, Agrosis stolonifera and Beckmannia eruciformis dominate, there are Althaea oicinalis, Carduus crispus, Euphorbia palustris, Geranium collinum, Inula germanica, Lysimachia nummularia, Lotus ucrainicus, Lythrum virgatum, Melica alissima, Plantago cornui, Trifolium pratense. In moderately saline habitats, there dominate Bolboschoenus mariimus, Festuca regeliana, Juncus gerardii, Puccinellia distans, Triglochin mariima. More saline habitats are occupied by communiies of Salicornia prostrata, Suaeda prostrata, Kochia prostrata. Eutrophic mires are dominated by Carex acuta, Carex acuiformis, Carex riparia, Phragmites australis; litoral vegetaion – Phragmites australis, Bolboschoenus mariimus, Typha angusifolia, Glyceria maxima; aquaic vegetaion – Potamogeton perfoliatus, Potamogeton pecinatus (Stuckenia pecinata), Myriophyllum vericillatum. Botanical significance. This area includes one of the largest and the southernmost natural steppe Pinus sylvestris wood in Ukraine. It includes also one of the largest loodplain oak woods. Important for poplar woods and inland halophyic vegetaion. Criterion C • E6.2 Continental inland salt steppes; area: 200 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 4500 ha; trend: decreasing; area data quality: medium; trend data quality: medium • G1.3 Mediterranean riparian woodland; area: 300 ha; trend: unknown; area data quality: poor; trend data quality: poor. • G1.414 Steppe swamp Alnus gluinosa woods; area: 300 ha; trend: stable; area data quality: poor; trend data quality: medium. • G3.4232 Sarmatic steppe Pinus sylvestris forests; area: 3000 ha; trend: decreasing; area data quality: medium; trend data quality: medium. Conservaion proposals. Create an Emerald Site a naional protected area including the enire IPA. Literature 1. Бельгард А.Л. Лесная растительность юго-востока УССР, Киев: Изд-во КГУ, 1950. – 264 с. 2. Екомережа степової зони України: принципи створення, структура, елементи / під ред. Д.В. Дубини і Я.І. Мовчана. – К., 2013. – С. 409 с. 258 Savranskyi Lis Ukrainian name: Савранський ліс. Transliteraion/Translaion variants: Savran' Forest. Area: 8475 ha. Altitude: 125–205 m. Latitude: 48°05'10" N (48.0862°). Longitude: 30°05'36" E (30.0934°). Administrative regions. Odesa region: Savran raion. Ownership: state, private (minor). Biogeographic regions: coninental. V.A. Onyshchenko Habitats. Level 1. G – 97.3%; H – 1.1%; I – 1.6%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 97.3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.1%; I1 Arable land and market gardens – 1.6%. Futher habitat description. G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – major, nature conservation and research – major. Protected areas: includes Savranskyi Lis state landscape reserve (8397 ha), same as Emerald Site "Savranskyi Lis". Threats: forestry (intensiied forest management) – medium. General description. Vegetaion consists of oak-hornbeam forests and termophilous oak forests. The tree layer is dominated by Quercus robur, Carpinus betulus, Quercus petraea. Frequent species are Acer campestre, Acer platanoides, Acer tataricum, Anemone ranunculoides, Asparagus tenuifolius, Cerasus avium, Corydalis solida, Euonymus europaeus, Euonymus verrucosus, Polygonatum hirtum, Pyrus communis, Scutellaria alissima, Swida sanguinea (Cornus sanguinea), Tilia cordata, Ulmus glabra, Ulmus minor. 259 Botanical significance. The largest termophilous deciduous forest in latland part of Ukraine. Criterion C G1.7 Thermophilous deciduous woodland (*91I0); area: 5000 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Create an Emerald including the enire IPA. Serbyno Ukrainian name: Сербино. Area: 1577 ha. Altitude: 150–243 m. Latitude: 47°53'23" N (47.8897°). Longitude: 29°26'34" E (29.4429°). Administrative regions. Odesa region: Balta raion. Ownership: state. Biogeographic regions: coninental. V.A. Onyshchenko Threats: forestry (intensiied forest management) – low. General description. Termophilous deciduous forest. Main dominants of the tree layer are Fraxinus excelsior and Quercus robur. Other frequent species are Acer campestre, Acer platanoides, Acer tataricum, Aegonychon purpureo-caeruleum, Anemone ranunculoides, Anthriscus sylvestris, Cerasus avium, Corydalis solida, Crataegus curvisepala s.l., Euonymus europaeus, Euonymus verrucosus, Polygonatum hirtum, Pyrus communis, Scutellaria alissima, Sambucus nigra, Swida sanguinea (Cornus sanguinea), Tilia cordata, Torilis japonica, Ulmus minor. Botanical significance. One of the largest termophilous deciduous forests in latland part of Ukraine. Criterion C G1.7 Thermophilous deciduous woodland (*91I0); area: 1500 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Create a state botanical reserve including the enire IPA. Sharivka Ukrainian name: Шарівка. Area: 44.4 ha. Altitude: 84–130 m. Latitude: 49°49’58” N (49.8327°). Longitude: 38°53’44” E (38.8955°). Administrative regions. Luhansk region: Bilokurakyne raion. Ownership: state. Habitats. Level 1. G – 99.0%; H – 1.0%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 99.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. G1.7 Thermophilous deciduous woodland; H5.6 Trampled areas. Land use: forestry – major. Protected areas: included in Emerald Site "Serbyno". 260 261 V.A. Onyshchenko, M.V. Banik Biogeographic regions: steppic. Habitats. Level 1. E – 73.0%; F – 2.0%; G – 5.0%; H – 20.0%. Habitats. Level 2. E1 Dry grasslands – 73.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 5.0%; H2 Screes – 20.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major. Protected areas: –. Threats: extracion (minerals/quarries) – low; forestry (aforestaion) – medium. General description. A hill with chalk outcrops and steppe vegetaion. Botanical significance. Important area for Hedysarum ucrainicum. Criterion A • Hedysarum ucrainicum Kaschm.; A(iv); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Conservaion proposals. Create a state botanical reserve. Literature 1. Banik M. Daphne’04. Final report. – Kharkiv, 2006. – 20 p. (http://www.rufford.org/ files/127.01.04%20Detailed%Final%20Report.pdf). woodland not on acid peat; G1.5 Broadleaved swamp woodland on acid peat; G1.7 Thermophilous deciduous woodland; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland. Land use: agriculture (animals) – minor, forestry – 30%; mowing / hay making – minor, nature conservation and research – major, tourism/recreaion – minor. Shatski Ozera V.A. Onyshchenko Ukrainian name: Шацькі озера. Transliteraion/Translaion variants: Shatsk Lakes. Area: 25003 ha. Altitude: 162–176 m. Latitude: 51°31’06” N (51.5184°). Longitude: 23°52’20” E (23.8723°). Administrative regions. Volynska region: Shatsk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 27%; D – 6%; E – 1%; F – 1%; G – 65%. Habitats. Level 2. C1 Surface standing waters – 25.5%; C3 littoral zone of inland surface waterbodies – 1.5%; D2 Valley mires, poor fens and transition mires – 1.8%; D5 Sedge and reedbeds, normally without free-standing water – 4.3%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 17%; G3 Coniferous woodland – 42%; G4 Mixed deciduous and coniferous woodland – 6%. Futher habitat description. C1.1 Permanent oligotrophic lakes, ponds and pools; C1.2 Permanent mesotrophic lakes, ponds and pools; C1.3 Permanent eutrophic lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D2.2 Poor fens and sot-water spring mires; D2.3 Transiion mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without freestanding water; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E3.4 Moist or wet eutrophic and mesotrophic grassland; E3.5 Moist or wet oligotrophic grassland; F9.2 Salix carr and fen scrub; G1.4 Broadleaved swamp 262 Protected areas: overlaps (24581 ha) with Shatskyi naional nature park, included in West Polesie biosphere reserve, overlaps (24581 ha) with Emerald Site “Shatskyi”. Threats: agricultural intensification/expansion (general) – low; development (recreaion/ tourism) – low, eutrophicaion – medium. General description. A complex of 17 lakes with adjacent forests and mires. The largest lakes are Sviiaz (2750 ha, maximum depth 58 m), Pulemetske (1635 ha, 4.4 m), Luky (675 ha, 3.2 m), Liutsymer (430 ha, 11 m), Ostrivyanske (250 ha, 3.8 m), Peremut (146 ha, 6.7 ha), Krymne (144 ha, 6 m), Pisochne (138 ha, 16 m). They are diferent in trophic indices (oligo-mesotrophic to eutrophic). Aquaic vegetaion is dominated mainly by Ceratophyllum demersum, Potamogeton crispus, Potanogeton lucens, Potamogeton pecinatus (Stuckenia pecinata), Elodea canadensis, Straiotes aloides, Nymphaea alba, Nymphaea candida, Nuphar lutea. There are charophyte communiies (Chara aspera, Ch. fragilis, Ch. delicatula, Ch. contraria, Lychnothamnus barbatus, Nitella symcarpa). Litoral vegetaion is dominated by Schoenoplectus lacustris (Scirpus lacustris), Phragmites australis, Glyceria maxima. Mires 263 belong predominantly to eutrophic and mesotrophic ones. Eutrophic mires are dominated by Carex elata, C. appropinquata, Phragmites australis, with presence of Potenilla palustris, Menyanthes trifoliata, Carex rostrata, Carex flava, Equisetum fluviatile, Lysimachia thyrsiflora. Mesotrophic mires are dominated by Carex lasiocarpa, Phragmites australis, Sphagnum fallax. Menyanthes trifoliata and Vaccinium oxycoccos (Oxycoccus palustris) are typical co-dominants. Oten there is an open layer of Pinus sylvestris and Betula bubescens. Swamp Alnus gluinosa forests occupy a large area. Their herb layer is dominated by Carex riparia, C. acutiformis, Iris pseudacorus. Typical species are Thelypteris palustris, Peucedanum palustre, Carex vesicaria, C. pseudocyperus, Stachys palustris. In more acidic habitats, there is a layer of peat mosses (Sphagnum centrale, S. squarrosum, S. obtusum). Wet Alnus gluinosa forests oten are co-dominated by Betula pendula, Populus tremula, Quercus robur, Fraxinus excelsior. Main species of the shrub layer are Frangula alnus and Corylus avellana. Typical species of the herb layer are Athyrium filix-femina, Urtica dioica, Festuca gigantea, Ficaria verna, Aegopodium podagraria, Asarum europaeum. Pine forests occupy the largest area. The most typical dominants of lower layers in mesic and wet Pinus sylvestris forests are Pleurozium schreberi, Vaccinium myrillus, Molinia caerulea. Constant species are Betula pendula, Calluna vulgaris, Dicranum polysetum, Frangula alnus, Quercus robur, Sorbus aucuparia, Vaccinium viis-idaea. In dry habitats, typical species are Thymus serpyllum, Festuca ovina, Jasione montana, Pilosella oicinarum (Hieracium pilosella). There occur acidophilous Quercus robur forests, acidophilous mixed oak-pine forests, and Betula pendula forests. Botanical significance. Important area for conservaion of diverse freshwater communiies, Aldrovanda vesiculosa, Dianthus pseudoseroinus. Criterion A • Aldrovanda vesiculosa L.; A(i), A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Dianthus pseudoseroinus Błocki; A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • C1.1 Permanent oligotrophic lakes, ponds and pools; area: 1000 ha; trend: decreasing (eutrophicaion); area data quality: poor; trend data quality: good. • C1.226 Floating Aldrovanda vesiculosa communities; area: <0.1 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C1.25 Charophyte submerged carpets in mesotrophic waterbodies; area: 10 ha; trend: decreasing (eutrophicaion); area data quality: poor; trend data quality: medium. • G3.1F Enclave Picea abies forests; area: 2 ha; trend: stable; area data quality: medium; trend data quality: poor. Conservaion proposals. Reduce the intensity of recreaion, the area of arable lands and the use of ferilizers in adjacent areas. Literature 1. Андрієнко Т.Л., Кузьмичов А.І., Прядко О.І. Болота в районі Шацьких озер // Укр. ботан. журн. – 1971. – 26, № 6. – С. 727–733. 2. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 215 с. 3. Борисова Е.В., Царенко П.М., Якушенко Д.Н. Современное состояние Charales озера Свитязь (Шацкий национальный природный парк, Волынское Полесье, Украина) // Альгология. – 2008. – 18, № 4. – С. 449–456 4. Борисова О.В., Гончаренко В.І. До вивчення Charales озер Шацького національного природного парку (Волинське Полісся) // Вісн. Львів. ун-ту. Сер.біол. – 2007, № 44. – С. 46–51. 5. Борисова О.В., Якушенко Д.М. Угруповання харових водоростей південнозахідного сектора озера Світязь (Волинське Полісся) // Укр. ботан. журн. – 2008. – 65, № 2. – С. 226–233. 6. Вірченко В.М. Бріофлора Шацького національного природного парку // Укр. ботан. журн. – 1999. – 56, № 1. – С. 67–73. 7. Водно-болотні угіддя України / Під ред. Г.Б. Марушевського, І.С. Жарук. – К.: Wetlands International Black Sea Programme, 2006. – 312 с. 8. Дідух Я.П., Фіцайло Т.В., Пашкевич Н.А., Мала Ю.І. Екологічні карти трилатерального біосферного резервату “Західне Полісся” (Шацький НПП) та їх аналіз // Укр. ботан. журн. – 2013. – Т. 70, № 4. – С. 450–456. 9. Дідух Я.П., Якушенко Д.М., Фіцайло Т.В. Класифікація рослинності та біотопів Української частини транскордонного біосферного резервату “Західне Полісся” // Створення транскордонного біосферного резервату та регіональної екологічної мережі в Поліссі. – К., 2008. – С. 41–56. 10. Карпова Г.О., Зуб Л.М. До поширення Aldrovanda vesiculosa L. на озерах Шацької групи // Ю.Д. Клеопов та сучасна ботанічна наука. Мат-ли читань, присвячених 100-річчю з дня народження Ю.Д. Клеопова. – К., 2002. – С. 375–378. 11. Прядко О.І., Онищенко В.А. НПП Шацький // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 548–557. 12. Цурик Є.І., Жижин М.П., Ященко П.Т. Поширення та охорона Picea abies (L.) Karsten у районі Шацьких озер // Укр. ботан. журн. – 1973. – 36, № 4. – С. 313–315. 13. Шацький національний природний парк. Наукові дослідження 1983–93 рр. – Світязь, 1994. – 248 с. 14. Шацький національний природний парк. Наукові дослідження 1994–2004 рр. – Луцьк, 2004. – 224 с. 15. Якушенко Д.М., Фіцайло Т.В., Коротченко І.А. Псамофітні екосистеми української частини біосферного резервату “Західне Полісся” // Стан і біорізноманіття екосистем Шацького національного природного парку: Мат-ли наук. конф. – Львів: СПОЛОМ, 2005. – С. 82–86. 16. Ященко П.Т. Флористична оцінка території Шацького природного національного парку // Укр. ботан. журн. – 1985. – 42, № 1. – С. 22–23. 17. Ященко П.Т. Судинні рослини Шацького національного природного парку // Шацький національний природний парк. Наукові дослідження 1983–1993 рр. – Світязь. – С. 132–163 с. 18. Ященко П.Т., Андрієнко Т.Л., Шеляг-Сосонко Ю.Р., Стойко С.М. Рослинний покрив Шацького природного парку // Укр. ботан. журн. – 1983. – 50, № 4. – С. 68–72. 264 265 Shebutynskyi Yar I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Шебутинський яр. Transliteraion/Translaion variants: Shebutynskyi Ravine. Area: 896 ha. Altitude: 115–275 m. Latitude: 48°33’03” N (48.5508°). Longitude: 27°10’49” E (27.1803°). Administrative regions. Chernivtsi region: Sokyriany raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 1%; G – 98%; H – 1% Habitats. Level 2. E1 Dry grasslands – 0.5%; E2 Mesic grasslands – 0.5%; G1 – Broadleaved deciduous woodland – 98.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Yar”, included in naional nature park “Khotynskyi”, overlaps (299 ha) with Emerald Site “Khotynskyi Naional Nature Park”. Threats: development (recreaion/tourism) – low. General description. Broadleaved forests dominated by Quercus robur with Carpinus betulus, Acer pseudoplatanus, Acer platanoides, Tilia cordata, Fraxinus excelsior, Cerasus avium, Sorbus torminalis. The shrub layer is composed of Acer tataricum, Acer campestre, Corylus avellana, Euonymus verrucosus, Euonymus europaeus, Sambucus nigra, Staphylea pinnata, Swida sanguinea (Cornus sanguinea), Viburnum lantana. Typical species of the herb layer are Carex pilosa, Stellaria holostea, Asarum europaeum, Aegopodium podagraria, Lathyrus vernus, Hedera helix, Hepatica nobilis. Botanical significance. Important area for Friillaria montana and Aconitum besserianum. Criterion А • Aconitum besserianum Andrz. ex Trautv; А (iiі); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. • Fritillaria montana Hoppe; А (ii); abundance: rare (1000 individuals); trend: stable; species data quality: good; trend data quality: poor. Literature 1. Волуца О.Д. Fritillaria montana Hoppe у флорі Чернівецької області // Науковий вісник Чернівецького університету: Збірник наукових праць. – Вип. 293: Біологія. – Чернівці: Рута, 2006. – С. 31–34. 2. Каземірська М.А. Стан популяції Fritillaria montana Hoppe (Liliaceae) на території ландшафтного заказника місцевого значення “Шебутинський яр” // Наукові основи збереження біотичної різноманітності: Матеріали десятої наукової конференції молодих учених (Львів, 7-8 жовтня 2010 року). – Львів, 2010. – С. 50–52. 3. Каземірська М.А., Чорней І.І. Fritillaria montana Hoppe (Liliaceae): географічна характеристика, поширення в Україні // Науковий вісник Чернівецького університету. Біологія (Біологічні системи). – 2010. – Т. 2, Вип. 3. – С. 63–68. 4. Каземірська М.А., Чорней І.І. Fritillaria montana Hoppe на території ландшафтного заказника місцевого значення “Шебутинський яр” // Молодь і поступ біології: збірник тез VI Міжнародної наукової конференції студентів і аспірантів (21-24 вересня 2010 року, м. Львів). – Львів, 2010. – С. 56–57. 5. Каземірська М.А., Чорней І.І. Вікова та просторова структури популяцій Fritillaria montana Hoppe у Прут-Дністровському межиріччі // Біологічні системи. – 2010. – Т. 2., Вип. 2. – С. 62–66. 6. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 7. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – C. 85–87. Sinozhai Futher habitat description. G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Land use: forestry – major, nature conservation and research – major. Protected areas: overlaps (about 790 ha) with regional landscape reserve “Shebutynskyi 266 I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Сіножаті. Area: 63.5 ha. Altitude: 285–325 m. Latitude: 48°36’05” N (48.6015°). 267 Longitude: 25°13’11” E (25.2198°). Administrative regions. Ivano-Frankivsk region: Horodenka raion, Kolomyia raion. Ownership: private, state. Biogeographic regions: coninental. Habitats. Level 1: E – 92.0%, F – 8.0%. Habitats. Level 2: E1 Dry grasslands – 75.0%; E2 Mesic grasslands – 17.0%, F3 Temperate Botanical significance. One of the best areas for Pulsailla grandis. There are other criterion A species: Adenophora liliifolia, Pulsailla patens. Criterion A • Adenophora liliifolia; A(ii); abundance: rare; trend: unknown; species data quality: good; trend data quality: poor. • Pulsailla grandis Wend.; A(ii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. • Pulsailla patens (L.) Mill.; A(ii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Conservaion proposals. Do not allow land plowing. Create a state botanical reserve and an Emerald Site. Skhidne Roztochia Ukrainian name: Східне Розточчя. Transliteraion/Translaion variants: Eastern Roztochchia. Area: 13680 ha. Altitude: 288–397 m. Latitude: 49°58’22” N (49.9728°). Longitude: 23°50’53” E (23.8479°). Administrative regions. Lviv region: Zhovkva raion, Yavoriv raion. and mediterranean-montane scrub – 8.0%. Futher habitat description: E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub. Land use: agriculture (animals) – minor. Protected areas: –. Threats: agricultural intensification/expansion (arable) – low. General description. Species-rich grassland with dominance of Brachypodium pinnatum, Calamagrostis arundinacea, Cirsium pannonicum, Festuca rupicola, F. valesiaca, Koeleria cristata, Molinia caerulea agg. Other frequent species: Adenophora lilifolia, Colchicum autumnale, Clematis recta, Galium boreale, Geranium sanguineum, Gymnadenia conopsea, Helictotrichon praeustum, Hypericum maculatum, Hypochaeris maculata (Achyrophorus maculatus), Inula hirta, Inula salicina, Knautia arvensis, Lathyrus pannonicus, Lilium martagon, Orchis ustulata, Peucedanum cervaria, Potentilla alba, Prunella grandiflora, Pulsatilla grandis, P. patens, Salvia pratensis, Sanguisorba officinalis, Scorzonera humilis, S. purpurea, Traunsteinera globosa, Trifolium alpestre, T. montanum, T. pannonicum. 268 269 V.A. Onyshchenko Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.2%; D – 0.4%; E – 0.3%; G – 98.6%; H – 0.5%. Habitats. Level 2. C1 Surface standing waters – 0.2%; D2 Valley mires, poor fens and transition mires – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.3%; E2 Mesic grasslands – 0.3%; G1 Broadleaved deciduous woodland – 77.7%; G3 Coniferous woodland – 2.8%; G4 Mixed deciduous and coniferous woodland – 18.1%. Futher habitat descripion. D2.3 Transiion mires and quaking bogs; E1.9 Open nonMediterranean dry acid and neutral grassland including inland dune grassland; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E3.5 Moist or wet oligotrophic grassland; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat, G1.6 Fagus woodland; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H5.6 Trampled areas. Land use: forestry – major, nature conservation and research – major. Protected areas: includes Roztochia nature reserve (2085 ha), overlaps (about 2920 ha) with Yavorivskyi naional nature park; includes Zavadivskyi regional landscape reserve (3561 ha), includes Hriada forest reserve (1149 ha), overlaps (about 5790 ha) with Roztochya biosphere reserve; includes Emerald Site “Roztochia Nature Reserve” (2085 ha), overlaps (about 2920 ha) with Emerald Site “Yavorivskyi Naional Nature Park”, overlaps (about 7820 ha) with Emerald Site “Zavadivskyi”, overlaps (about 855 ha) with Emerald Site “Roztochia”. Threats: forestry (intensiied forest management) – low; development (recreaion/tourism) – low. General description. Major vegetaion type is the Fagus sylvaica forest. Dominants of the herb layer are Anemone nemorosa, Asarum europaeum, Carex pilosa, Convallaria majalis, Lamium galeobdolon, Maianthemum bifolium. Other species of high constancy are Acer platanoides, Acer pseudoplatanus, Athyrium ilix femina, Carex digitata, Dryopteris carthusiana, Dryopteris ilix-mas, Melica nutans, Galium odoratum, Polytrichum formosum, Quercus robur, Rubus hirtus. Signiicant areas are covered by the Carpinus betulus – Quercus robur forests, Quercus robur – Pinus sylvestris forests, Pinus sylvestris forests. Dominants of acidophilous Quercus robur – Pinus sylvestris forests are Convallaria majalis, Maianthemum bifolium, Vaccinium myrillus. Dominants of the Pinus sylvestris forests are Vaccinium myrillus, Pleurozium schreberi. Other constant species are Dicranum polysetum, Luzula pilosa, Melampyrum pratense, Trientalis europaea (Lysimachia europaea), Vaccinium viisidaea. Botanical significance. Important area for latland beech forests. Criterion C • G1.6 Fagus woodland (excluding G1.66); area: 8300 ha; trend: increasing; area data quality: medium; trend data quality: good. Literature 1. Данилків І.С., Сорока М.І. Мохоподібні державного заповідника “Розточчя”. Препр. – Львів, 1989. – 78 с. 2. Жижин М.П., Кагало О.О., Чабан Х.І. Рослинність урочища Заливки заповідника Розточчя // Укр. ботан. журн. – 1988. – 45, № 1. – С. 68–72. 270 3. Кагало О.О. ПЗ Розточчя // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 325–335. 4. Кагало О.О. НПП Яворівський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 558–565. 5. Сорока М.І. Судинні рослини державного заповідника Розточчя. – Львів, 1990. – С. 81–85. 6. Сорока М.І. Синтаксономія рослинності Українського Розточчя // Науковий вісник УкрДЛТУ. – Львів, 1998, вип. 7. – С. 37–41. 7. Сорока М.І. Рослинність Українського Розточчя. – Львів: Вид-во “Світ”, 2008. – 432 с. 8. Ткачик В. Рослинність заповідника “Розточчя”: ідентифікація сучасного розмаїття фітоценозів. – Львів: НТШ, 1997. – 120 с. 9. Ткачик В.П. Рослинність заповідника “Розточчя”: класифікація методом БраунБланке. – Львів: НТШ, 1999. – 198 с. Skhidnyi Churiuk V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Східний Чурюк. Transliteraion/Translaion variants: Eastern Churyuk. Area: 2210.0 ha. Altitude: 0–13 m. Latitude: 46°07’00” N (46.1166°). Longitude: 34°15’36” E (34.2600°). Administrative regions. Kherson region: Novotroitske raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 58.8%; E – 41.2%. Habitats. Level 2. A2 Littoral sediment – 3.0%; A5 Sublittoral sediment – 55.8%; E1 Dry grasslands – 37.2%; E6 Salt steppes – 4.0%. Futher habitat description. A2.3 Littoral mud; A2.5 Coastal saltmarshes and saline reedbeds; A5.3 Subittoral mud; E1.2 Perennial calcareous grassland and basic steppes; E6.2 Continental inland salt steppes. Land use: nature conservaion and research – 100%. Protected areas: included in Azovo-Syvaskyi naional nature park (zone of strict protecion), included in Ramsar Site “Central Syvash”, included in Emerald Site “Azovo-Syvaskyi Naional Nature Park”. Threats: abandonment/reducion of land management – low, natural events: erosion – medium. General description. A loess island in the Syvash Bay with adjacent waters. Major vegetaion type on the Churiuk island is the steppe. Dominant species are Stipa lessingiana, S. capillata, S. ucrainica, Agropyron pectinatum, Festuca valesiaca. Other frequent species are Achillea setacea, Crinitaria villosa, Dianthus elongatus, Elisanthe viscosa, Hesperis trisis, Linaria macroura, Malabaila graveolens, Phlomis pungens, Tanacetum millefolium, Valeriana tuberosa, Vicia angusifolia, Vicia cracca. In depressions, there dominate Elytrigia repens, 271 Elytrigia intermedia, Leymus ramosus, Festuca valesiaca, Poa angusifolia. In the salt steppe, dominant species are Artemisia santonica, Festuca valesiaca, Caroxylon laricinum, Kochia prostrata, Ephedra distachya. In mesic and wet halophyic communiies, there prevail Puccinellia fominii, Limonium meyeri, Artemisia santonica. Peripheral part of the island is occupied by solonchaks dominated by Halocnemum strobilaceum, Lepidium crassifolium, Limonium sufruicosum, Petrosimona brachiata, Puccinellia fominii, Salicornia perennans. 2. Коломійчук В.П. Рідкісні види судинних рослин Азово-Сиваського національного природного парку // Вісті біосферного заповідника “Асканія-Нова”. – 2002. – №4. – С. 37–44. 3. Коломійчук В.П. Азово-Сиваський національний природний парк // Фіторізноманіття національних природних парків України / під ред. Т.Л. Андрієнко та В.А. Онищенка. – К.: Науковий світ, 2003. – C. 19–28. 4. Коломійчук В.П. Рідкісні рослинні угруповання островів Сиваша // Укр. ботан. журн. – 2003. – 60, № 5 – С. 540–545. 5. Коломійчук В.П. Азово-Сиваський національний природний парк // Фіторізноманіття національних природних парків України / під ред. Т.Л. Андрієнко та В.А. Онищенка. – К.: Науковий світ, 2003. – C. 19–28. 6. Коломійчук В. П., Онищенко В. А., Перегрим М. М. Важливі ботанічні території Приазов’я / за ред. Т.Л. Андрієнко. – К. : Альтерпрес, 2012. – 114 с. Skhyly Kohylnyka Ukrainian name: Схили Когильника. Transliteraion/Translaion variants: Kohyl’nyk Slopes. Area: 2683 ha. Altitude: 40–180 m. Latitude: 46°14’24” N (46.2400°). Botanical significance. One of the best sites for endemic species Lepidium syvaschicum (locus classicus, globally ~10 localiies), Allium scythicum (globally ~10 localiies). One of the best examples of the southern Ukrainian steppes. Criterion A • Allium scythicum Zoz.; A(iii); abundance: rare; trend: luctuaing; species data quality: medium; trend data quality: poor. • Lepidium syvaschicum Kleopow; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 800 ha; trend: slow decreasing; area data quality: good; trend data quality: good. Literature 1. Бойко М.Ф. Раритетне фіторізноманіття Херсонщини (Україна) та його охорона // Чорноморський ботанічний журнал. – 2005. – 1, №1. – С. 53–59. 272 273 V.A. Onyshchenko, O.M. Popova Longitude: 29°04’26” E (29.0739°). Administrative regions. Odesa region: Tarutyne raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. E – 84%; G – 16%. Habitats. Level 2. E1 Dry grasslands – 84%; G1 Broadleaved deciduous woodland – 16%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; G1.7 Thermophilous deciduous woodland (minor); G1.C Highly artificial broadleaved deciduous forest plantations. Land use: agriculture (animals) – major, forestry – major. Protected areas: included in Emerald Site “Besarabskyi Kolkhikum”. Threats: forestry (aforestaion) – high. General description. The area is situated on the slope of the Kohylnyk river’s valley. Major habitat type is the steppe. A signiicant part of the area is occupied by forest plantaions of Gleditschia triacanthos and Robinia pseudoacacia. Fragments of natural termophilous Fraxinus excelsior woods occur. Botanical significance. The area is noted for conservaion of Colchicum fominii. Criterion A • Colchicum fominii Bordz; A(ii), A(iv); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Create an Emerald Site. Land use: agriculture (animals) – major; forestry – minor; nature conservaion and research – major. Protected areas: overlaps (about 350 ha) with Honcharivskyi regional botanical reserve Skhyly Krasnoi i Kobylky V.A. Onyshchenko Ukrainian name: Схили Красної і Кобилки. Transliteraion/Translaion variants: Krasna and Kobylka Slopes. Area: 663.9 ha. Altitude: 80–130 m. Latitude: 49°30’50” N (49.5138°). Longitude: 38°08’12” E (38.1367°). Administrative regions. Luhansk region: Svatove raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 83.7%; F – 2.0%; G – 6.2%; H – 5.1%; I – 3.0%. Habitats. Level 2. E1 Dry grasslands – 78.7%; E2 Mesic grasslands – 5.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 6.2%; H2 Screes – 5.1%; I1 Arable land and market gardens – 3.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.2 Low and medium alitude hay meadows; E2.5 Meadows of the steppe zone; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Mesoand eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultrabasic screes of warm exposures; I1.5 Bare illed, fallow or recently abandoned arable land. 274 Threats: agricultural intensification/expansion (arable) – low, extracion (minerals/quarries) – low; forestry (aforestaion) – low. General description. Slopes of the valleys of the Krasna and Kobylka rivers with the steppe vegetaion, outcrops of chalk and oak woods. Dominants of the chalk outcrops are Artemisia hololeuca, Artemisia salsoloides, Hyssopus cretaceus, Silene cretacea, Silene supina, Thymus cretaceus. Other typical species are Asperula tephrocarpa, Bupleurum falcatum, Cephalaria uralensis, Gypsophila oligosperma, Pimpinella titanophila, Teucrium polium. Botanical significance. Important area for conservaion of chalk outcrops with endemic species. Criterion A • Linaria cretacea Fisch. ex Spreng.; A(iv); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. • Silene cretacea Fisch. ex Spreng.; A(ii), A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. 275 Conservaion proposals. Create an Emerald Site including the enire IPA. Literature 1. Природно-заповідний фонд Луганської області // О.А. Арапов (заг. ред.), Т.B. Сова, О.А. Cавенко, В.Б. Фєрєнц, Н.У. Кравець, Л.Л. Зятьков, Л.О. Морозова. Довідник. – 3-е вид., доп. і перероб. – Луганськ: “Луганська правда”, 2013. – 224 с. Slovechanskyi Kriazh V.A. Onyshchenko Ukrainian name: Словечанський кряж. Transliteraion/Translaion variants: Slovechanskyi Ridge, Slovechno Ridge. Area: 6119.0 ha. Altitude: 187–191 m. Latitude: 51°20’18” N (51.3384°). Longitude: 28°12’25” E (28.2069°). Administrative regions. Zhytomyr region: Ovruch raion. G1 Broadleaved deciduous woodland – 57.3%; G3 Coniferous woodland – 30.9%; G4 Mixed deciduous and coniferous woodland – 10.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%; J4 Transport networks and other constructed hard-surfaced areas – 0.1%. Futher habitat description. D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; G1.4 Broadleaved swamp woodland not on acid peat; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Nonriverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – major. Protected areas: included in Slovechanskyi Kriazh regional forest reserve, included in Emerald Site “Slovechanskyi Kriazh”. Threats: forestry (intensiied forest management) – low. General description. Major vegetaion types are acidophilous forests dominated by Quercus robur, Pinus sylvestris, Betula pendula. In the herb layer, there dominate Calamagrosis arundinacea, Maianthemum bifolium, Oxalis acetosella, Vaccinium myrillus. In pine forests, there is a moss layer dominated by Pleurozium shreberi and Dicranum polysetum. Smaller areas are covered by Quercus petraea and Alnus gluinosa forests. Botanical significance. Important for conservaion of acidophilous oak forests. Criterion C • G1.8 Acidophilous Quercus-dominated woodland; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: medium. Somyno Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 0.5%; G – 98.9%; H – 0.5%; J – 0.1%. Habitats. Level 2. D5 Sedge and reedbeds, normally without free-standing water – 0.5%; V.A. Onyshchenko Ukrainian name: Сомино. Area: 10852 ha. Altitude: 146–160 m. Latitude: 51°25’22” N (51.4228°). Longitude: 26°55’11” E (26.9197°). Administrative regions. Rivne region: Sarny raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. C – 1%; D – 60%; F – 1%; G – 38%. Habitats. Level 2. C1 Surface standing waters – 1%; D2 – Valley mires, poor fens and transition mires – 59%; D5 Sedge and reedbeds, normally without free-standing water – 1%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 10% G3 Coniferous woodland – 18%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D2.3 Transition mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.7 Closed non-Mediterranean dry acid and neutral grassland; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; F9.2 Salix carr and fen scrub; G1.5 Broadleaved swamp woodland on 276 277 acid peat; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.4 Mixed Pinus sylvestris – Betula woodland. Land use: nature conservation and research – 100%. • D2.3 Transition mires and quaking bogs; area: 6400 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.51 Sphagnum Betula woods; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Андрієнко Т.Л. ПЗ Рівненський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 313–324. 2. Андрієнко Т.Л., Прядко О.І. Болотний масив Сомино на Ровенщині, його наукова і господарська цінність // Укр. ботан. журн. – 1980. – 36, № 4. – С. 65–69. 3. Андрієнко Т.Л., Прядко О.І., Онищенко В.А. Раритетна компонента флори Рівненського природного заповідника // Укр. ботан. журн. – 2006. – 63, № 2. – С. 220–228. 4. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 215 с. 5. Водно-болотні угіддя України / під ред. Г.Б. Марушевського та І.С.Жарук. – К.: Чорноморська програма Ветландс Інтернешнл, 2006. – 312 с. 6. Онищенко В.А., Андрієнко Т.Л., Прядко О.І. Рослинність ділянки Сомино Рівненського природного заповідника // Науковий вісник Волинського національного університету імені Лесі Українки. Біологічні науки. – 2009. – № 9. – С. 173–187. 7. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Sovyi Yar Protected areas: included in Rivnenskyi nature reserve, included in Emerald Site “Rivnenskyi Nature Reserve”. Threats: –. General description. Transiion mire dominated by Carex lasiocarpa and peat mosses (Sphagnum centrale, S. fallax, S. cuspidatum, S. subsecundum, S. magellanicum, S. palustre). Species of high constancy are Eriophorum gracile, Lysimachia thyrsilora, Lysimachia vulgaris, Menyanthes trifoliata, Pedicularis palustris, Peucedanum palustre, Phragmites australis, Potenilla palustris, Rhynchospora alba; in more oligotrophic condiions – Andromeda polifolia, Drosera rotundifolia, Vaccinium oxycoccos (Oxycoccus palustris); in more eutrophic condiions – Carex elata, Cnidium dubium, Lythrum salicaria, Mentha arvensis. A porion of the mire has a tree layer of Betula pubescens. In some places, Carex rostrata, Phragmites australis, Eriophorum gracile, Carex omskiana dominate. Higher levels are occupied by Pinus sylvestris woods. Botanical significance. One of the largest transiion mires in Ukraine. Criterion C 278 V.A. Onyshchenko Ukrainian name: Совий яр. Transliteraion/Translaion variants: Sovii Ravine. Area: 1081.0 ha. Altitude: 125–280 m. Latitude: 48°39’49” N (48.6636°). Longitude: 26°53’11” E (26.8863°). Administrative regions. Khmelnytskyi region: Kamianets-Podilskyi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 0.3%; E – 1.5%; G – 96.2%; H – 1.0%; I – 0.5%; J – 0.5%. Habitats. Level 2. C2 Surface running waters – 0.3%; E1 – Dry grasslands – 0.7%; E2 – Mesic grasslands – 0.8%; G1 Broadleaved deciduous woodland – 94.4%; G3 Coniferous woodland – 0.2%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, earlystage woodland and coppice – 1.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Land use: forestry – major, nature conservaion and research – major Protected areas: includes Sovyi Yar state landscape reserve (827 ha), included in Podilski 279 Tovtry naional nature park, included in Emerald Site “Podilski Tovtry Naional Nature Park”. Threats: –. General description. A wood with the dominance of Quercus robur and Carpinus betulus in the tree layer. Botanical significance. Important for endemic species Aconitum besserianum. Criterion A • Aconitum besserianum Andrz. ex Trautv.; A(iii); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. Literature 1. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Striltsivskyi Step Ukrainian name: Стрільцівський степ. Transliteraion/Translaion variants: Stril’tsivs’kyi Steppe. Area: 1036.5 ha. Altitude: 120–182 m. Latitude: 49°17’35” N (49.2930°). Longitude: 40°04’43” E (40.0786°). 280 V.A. Onyshchenko Administrative regions. Luhansk region: Milove raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 68.3%; D – 0.03%; F – 31.0%; G – 0.4%; H – 0.2%. Habitats. Level 2. D5 Sedge and reedbeds, normally without free-standing water – 0.03%; E1 Dry grasslands – 67.8%; E2 Mesic grasslands – 0.5%; E6 Inland salt steppes – 0.02%; F3 Temperate and mediterranean-montane scrub – 31.0%; F9 Riverine and fen scrubs – 0.01%; G1 Broadleaved deciduous woodland – 0.4%; H2 Screes – 0.02%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; E6.2 Continental inland salt steppes; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; F9.1 Riverine scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.C Highly artificial broadleaved deciduous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservaion and research – 100%. Protected areas: included in Luhanskyi nature reserve (same as Striltsivskyi Step division of the reserve), included in Emerald Site “Luhanskyi Nature Reserve”. Threats: abandonment/reducion of land management – low. General description. The predominant vegetaion of the area is the steppe, both virgin (446 ha) and old fallows (270 ha). The second major vegetaion type is the steppe shrubs (320 ha). Among the steppe communiies the shrub steppes have the largest area. The most common combinaions of dominants are Sipa irsa with Caragana frutex or Amygdalus nana, less common – with Chamaecyisus ruthenicus. Steppes without co-dominance of shrubs also occupy a large area. Usually they are dominated by Sipa irsa and Sipa zalesskii. Another 281 important species: Achillea pannonica, Adonis wolgensis, Bromopsis riparia, Elytrigia intermedia, Elytrigia sipifolia, Elytrigia trichophora, Festuca rupicola, Galatella villosa, Helictotrichon schellianum, Hierochloe repens, Koeleria cristata, Limonium platyphyllum, Medicago romanica, Phleum phleoides, Phlomoides tuberosa (Phlomis tuberosa), Poa angusifolia, Potenilla schuri, Salvia nutans, Salvia stepposa, Sipa capillata, Sipa dasyphylla, Sipa pennata, Sipa pulcherrima, Veronica spicata. Besides there occur Sipa pulcherrima steppes with calciphilous species Astragalus albicaulis, Gypsophila oligosperma, Hedysarum grandilorum, Onosma tanaiica, Rhaponicoides ruthenica (Centaurea ruthenica); sand steppes dominated by Sipa borysthenica and Festuca beckeri with Artemisia marschalliana, Astragalus varius, Jurinea centauroides, Potenilla incana, Pulsailla patens, Pulsailla pratensis; salt steppes dominated by Festuca valesiaca and Galatella dracunculoides with Artemisia santonica, Bulbocodium versicolor (Colchicum versicolor), Ferula tatrica, Kochia prostrata, Tulipa ophiophylla. Shrub vegetaion is represented by the steppe shrubs (Prunus stepposa, Caragana frutex, Amygdalus nana, Chamaecyisus ruthenicus), the wood shrubs with small trees (Acer tataricum, Euonymus europaeus, Euonymus verrucosus, Malus praecox, Rhamnus catharica, Sambucus nigra, Swida sanguinea (Cornus sanguineus), Ulmus laevis, Ulmus pumila) and the loodplain Salix triandra and Salix cinerea shrubs (small area). Forest vegetaion (4 ha) is represented by ariicial forest belts (Fraxinus lanceolata) and loodplain Salix alba woods. Botanical significance. Important area for conservaion of steppe shrubs and steppes. Criterion A • Diplotaxis cretacea Kotov; A(iv); abundance: occasional; trend: stable; species data quality: good; trend data quality: medium. • Paeonia tenuifolia L.; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 710 ha; trend: decreasing; area data quality: good; trend data quality: good. • F3.247 Ponto-Sarmatic deciduous thickets; area: 150 ha; trend: increasing; area data quality: medium; trend data quality: medium. Literature 1. Білик Г.І., Ткаченко В.С. Рослинний покрив Стрільцівського степу // Укр. ботан. журн. – 1971. – 28, № 5. – С. 613–617. 2. Біорізноманітність Луганського природного заповідника НАН України / сост. Т. Сова. – Луганськ: ЛГСІ, 2005. – 218 с. 3. Биоразнообразие Луганского природного заповедника: растительный мир / Составители: Сова Т. В., Русина Н. В., Гузь Г. В., Боровик Л. П., Шиян-Глотова А. В. – Луганск: Элтон–2, 2009. – 130 с. 4. Бойко М.Ф. Мохоподібні заповідників “Стрільцівський степ” і “Михайлівська цілина” // Укр. ботан. журн. – 1981. – 38, № 4. – С. 27–31. 5. Боровик Л.П. Природні та антропогенні фактори демутації перелогів на території Стрільцівського степу (відділення Луганського природного заповідника) // Чорноморський ботан. журн. – 2008. – 4, № 1. – С. 98–106. 6. Боровик Л.П. Растительность залежей как важный компонент сохранения биоразнообразия на востоке Украины (Луганская область) // Вісник Одеського національного університету. – 2008. – 13, вып. 16. – С. 69–73. 7. Боровик Л.П. Постпирогенная динамика растительных сообществ Стрельцовской степи // Збірка тез доповідей міжнародної конференції V-ї ботанічні читання пам’яті Й.К. Пачоського. – Херсон: Айлант. – 2009. – С. 101. 8. Кондратюк Е.Н., Бурда Р.И., Чуприна Т.Т., Хомяков М.Т. Луганский гocударственный заповедник. Растительный мир. – Киев: Наук. думка, 1988. – 188 с. 9. Маслова В.Р. Ліхенофлора Провальского степу // Зб. наук. праць “Інтродукція і акліматизація рослин на Україні”. – 1979. – Вип. 15. – С. 51–54. 10. Приходькова Л.П. Синьозелені водорості в грунтах заповідника “Провальський степ” // Укр. ботан. журн. – 1988. – 45, № 2. – С. 9–13. 11. Русіна Н.В. Історія та сучасний стан дослідження ліхенобіоти Луганського природного заповідника // Наукові праці Луганського природного заповідника. Рослинний і тваринний світ та його охорона. – Луганськ. – 2011. – Вип. 2. – С. 47–53 12. Русина Н.В., Ходосовцев А.Е. Лихенобиота Стрельцовской cтепи // VI міжнародна наукова конференція “Промислова ботаніка: стан та перспективи розвитку”. – Донецьк. – 2010. – 405–407. 13. Сова Т.В., Боровик Л.П. ПЗ Луганський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 221–253. 14. Ткаченко В.С., Чуприна Т.Т., Бакланов О.В. Заповідник Провальський степ (сучасний стан і завдання наукових досліджень) // Укр. ботан. журн. – 1979. – 36, № 4. – С. 352–356. 15. Ткаченко В.С. Изучение особенностей резерватных сукцессий Стрельцовской степи по материалам периодического картирования // Геоботаническое картографирование. – 1989. – С. 47–61. 16. Ткаченко В.С. Особливості екотопічних змін та механізму становлення потенційних фітоценоструктур Стрільцівського степу // Укр. ботан. журн. – 1996. – 53, № 5. – С. 527–535. 17. Ткаченко В.С. Прогноз розвитку рослинності та збереження біорізноманітності “Стрільцівського степу” // Укр. ботан. журн. – 1996. – 53, № 6. – С. 645–652. 18. Ткаченко В.С. “Стрільцівський степ” в фітоценотичному моніторингу Старобільських степів // Вісті Біосферного заповідника “Асканія-Нова”. – 2009. – Т. 11. – С. 6–19. 19. Ткаченко B.C., Боровик Л.П., Сова Т.В., Лисенко Г.М. Структура рослинного покриву ділянки розширення “Стрільцівського степу” (Луганська обл., Україна) // Вісті Біосферного заповідника “Асканія-Нова”. – 2009. – Т. 11. – С. 35–47. 20. Ткаченко B.C., Сова Т.В., Боровик Л.П. Еколого-генетичний ряд рослинності “Стрільцівського степу” на Луганщині // Зб. ст. до 100-річчя д.б.н., проф. Г.І. Білика “Степові і галофітні екосистеми України”. – К. – 2004. – С. 595–620. 21. Ткаченко В.С., Чуприна Т.Т. Зміни в рослинному покриві Стрільцівського степу за даними фітоценологічного моніторингу // Укр. ботан. журн. – 1995. – 52, № 2. – С. 252–259. 282 283 Stuzhytsia Ukrainian name: Стужиця. Area: 11208 ha (10072.0) ha. Altitude: 355–1250 m. Latitude: 49°02’04” N (49.0344°). Longitude: 22°39’32” E (22.6589°). Administrative regions. Zakarpatska region: Velykyi Bereznyi raion. Ownership: state, private. Biogeographic regions: alpine. V.A. Onyshchenko Habitats. Level 1. C – 0.1%; D – 0.1%; E – 24.3%; G – 74.4%; H – 1.0%. Habitats. Level 2. C2 Surface running waters – 0.1%; D2 Valley mires, poor fens and transition mires – 0.1%; E1 Dry grasslands – 4.5%; E2 Mesic grasslands – 17.0%; E3 Seasonally wet and wet grasslands – 0.8%; E5 Woodland fringes and clearings and tall forb stands – 2.0%; G1 Broadleaved deciduous woodland – 70.0%; G3 Coniferous woodland – 1.3%; G4 Mixed deciduous and coniferous woodland – 3.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; D2.2 Poor fens and soft-water spring mires; E1.7 NonMediterranean dry acid and neutral closed grassland; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E4.3 Acid alpine and subalpine grassland; E5.2 Thermophile woodland fringes; E5.4 Moist or wet tall-herb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; G1.6 Fagus woodland; G3.F Highly artificial coniferous plantations; G4.6 Mixed Abies – Picea 284 – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H5.6 Trampled areas. Land use: agriculture (animals) – minor, forestry – minor, mowing/hay making – 25%; nature conservation and research – major. Protected areas: included in Uzhanskyi naional nature park, overlaps with World Heritage Site “Primeval Beech Forests of the Carpathians and the Ancient Beech Forests of Germany” (6147 ha; core zone: 2532 ha, bufer zone: 3615 ha), included in biosphere reserve “East Carpathians”, included in Emerald Site “Uzhanskyi Naional Nature Park”. Threats: abandonment/reducion of land management – low, agricultural intensification/ expansion (general) – low. General description. The largest area is covered by Fagus sylvaica forests. Dominants of the herb layer are Dentaria glandulosa, Dentaria bulbosa, Dryopteris filix-mas, Galium odoratum, Lamium galeobdolon, Rubus hirtus, Symphytum cordatum. Other typical species are Actaea spicata, Anemone nemorosa, Anemone ranunculoides, Corydalis cava, Corydalis solida, Oxalis acetosella, Polygonatum verticillatum, Salvia glutinosa, Senecio ovatus. In acidophilous beech forests, the herb layer consists mainly of Luzula luzuloides, Luzula sylvatica, Prenanthes purpurea, Rubus hirtus, Festuca drymeja, Galium odoratum, Dryopteris filix-mas, Oxalis acetosella, Maianthemum bifolium. On the steep slopes with stony soils, there are forests dominated by Acer pseudoplatanus with signiicant paricipaion of Ulmus glabra. Their typical species are Sambucus nigra, Ribes uva-crispa, Rubus hirtus, Pulmonaria obscura, Glechoma hirsuta, Polystichum braunii, Phyllitis scolopendrium, Dryopteris filix-mas. Hay meadows are dominated by Arrhenatherum elatior, Festuca rubra, Cynosurus cristatus. Other typical species are Campanula patula, Galium mollugo, Knautia arvensis, Crepis biennis. Botanical significance. One of the best areas of beech forests in Ukraine. A good example of mountain low and medium alitude hay meadows. Criterion C • E2.2 Low and medium alitude hay meadows; area: 1350 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.6 Fagus woodland; area: 8100 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.A4 (*9180) Ravine and slope woodland; area: 50 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Hadač E., Stoyko S.M., Terray J., Tasenkevich L., Bural M. Notes on plant communities of the protected complex Stuzhytsia – a part of the trilateral Polish-Slovakian-Ukrainian biosphere reserve “The Eastern Carpathians” // Укр. ботан. журн. – 1995. – 52, № 5. – С. 686–695. 2. Hadač E., Stoyko S.M., Terray J., Tasenkevich L., Bural M. Notes on the flora and vegetation of the botanical reserve “Stinka” (Biosfere reserve “The Eastern Carpathians”) // Укр. ботан. журн. – 1996. – 53, № 1/2. – С. 105–111. 3. Кваковська І.М. НПП Ужанський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 506–518. 4. Крічфалушій В.В., Лесьо І.М. Раритетні види рослин Ужанського національного природного парку // Укр. ботан. журн. – 2004. – 61, № 1. – С. 27–35. 5. Ужанський національний природний парк / Крічфалушій В.В., Луговой О.Є., Іванега І.Ю. та ін. – Ужгород: ЕкоЦентр – Тиса, 2001. – 120 с. – (Серія “Збереження біорізноманіття”: кн. 5). 285 6. Ужанський національний природний парк. Поліфункціональне значення / С.М. Стойко, Е. Гадач, Л.О. Тасєнкевич та ін.; під ред. С.М. Стойко. – Львів: Меркатор, 2007. – 306 с. 7. Устименко П.М., Попович С.Ю. Продромус рослинності Стужицького масиву Карпатського біосферного заповідника // Укр. ботан. журн. – 1995. – 52, № 3. – С. 414– 419. 8. Устименко П.М., Попович С.Ю. Висотна диференціація рослинності Стужицького масиву Карпатського біосферного заповідника // Укр. ботан. журн. – 1996. – 53, № 3. – С. 703–707. 9. Фіторізноманіття національних природних парків України / Під заг. ред. Т.Л. Андрієнко та В.А. Онищенка. – Київ: Науковий світ, 2003. – 143 с. Sviai Hory Ukrainian name: Святі гори. Transliteraion/Translaion variants: Svyai Gory, Holy Hills. Area: 18207.0 ha. Altitude: 58–211 m. Latitude: 49°01’52” N (49.0311°). Longitude: 37°31’30” E (37.5250°). 286 V.A. Onyshchenko Administrative regions. Donetsk region: Sloviansk raion, Lyman (Krasnyi Lyman) raion Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.4%; D – 0.1%; E – 1.2%; F – 0.1%; G – 96.5%; H – 1.5% , J – 0.2% Habitats. Level 2. C1 Surface standing waters – 0.1%; C2 Surface running waters – 0.2%; C3 Littoral zone of inland surface waterbodies – 0.1%; D5 Sedge and reedbeds, normally without free-standing water – 0.1%; E1 Dry grasslands – 0.1%; E2 Mesic grasslands – 0.1%; E3 Seasonally wet and wet grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 0.1%; G1 Broadleaved deciduous woodland – 61.9%; G3 Coniferous woodland – 26.5%; G4 Mixed deciduous and coniferous woodland – 9.2%; H2 Screes – 0.01%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.5%; J4 Transport networks and other constructed hard-surfaced areas – 0.2%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; E1.2 Perennial calcareous grassland and basic steppes; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; F3.1 Temperate thickets and scrub; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas; J4.2 Road networks; J4.3 Rail networks. Land use: mowing/hay making – 1%; forestry – 85%; nature conservaion and research – 100%; tourism and recreaion – minor. Protected areas: included in Sviai Hory naional nature park and Emerald Site “Sviai Hory” (a part of this park belongs to IPA “Zaplava Siverskoho Dintsia”). Threats: development (recreaion/tourism) – low; forestry (aforestaion) – low. General description. The area includes the loodplain of the Siverskyi Donets river (762 ha, medium part of the IPA), sand terrace over the loodplain (7602 ha, northern part) and plateau (2666 ha, southern part). In the loodplain, there prevail Quercus robur forests, lesser areas are covered by Alnus gluinosa and Populus alba forests. Floodplain meadows are dominated by Festuca pratensis, Elytrigia repens, Koeleria delavignei, Phleum pratense, Poa pratensis, Beckmanioa eruciformis, Carex praecox. Dominants of wet habitats are Carex riparia, Phalaroides arundinacea, Phragmites australis, Carex melanostachya, Eleocharis palustris. Sand terrace is occupied by Pinus sylvestris and Pinus silvestris – Quercus robur forests, in depressions – Alnus gluinosa woods. The major dominant of the herb layer in pine forests is Calamagrosis epigeios, other species of high constancy are Pilosella oicinarum, Rumex acetosella, Solidago virgaurea, Tanacetum vulgare. Sand grasslands occupy small area due to ariicial aforestaion. Their dominants are Artemisia tschernieviana, Carex colchica, Festuca beckeri, Koeleria sabuletorum, Thymus pallasianus. South of the Siverskyi Donets river, there are mesic forests dominated by Quercus robur, Fraxinus excelsior, with co-dominance of Acer campestre, Acer platanoides, Tilia cordata. Other constant species: Anemone ranunculoides, Asarum europaeum, Corydalis solida, Corylus avellana, Dentaria quinquefolia, Euonymus europaeus, Euonymus verrucosus, Galium odoratum, Lathyrus vernus, Polygonatum mulilorum, Pulmonaria obscura, Scilla sibirica, Stellaria holostea, Ulmus minor. Insigniicant area is occupied by outcrops (screes) of chalk which are rich in 287 endemic species. Condiion of broadleaved forests of the southern porion of the territory is good. A big part of them belongs to the zone of strict protecion of the naional park, another part – to the zone of regulated recreaion. Mean age of the tree layer is about 90 years. Condiion of pine woods is medium, but it is beter than in most other places of Ukraine. The tree layer is mainly of ariicial origin (plantaion of Pinus sylvestris). Species composiion has natural character and includes endemic species. Northern part of IPA belongs predominantly to the zone of regulated recreaion that does not allow forest clearing. Eforts to establish Pinus sylvestris plantaions prevent forming sand steppes which previously occupied a much larger area. Botanical significance. Important for conservaion of steppe pine forests, mesic deciduous forests and steppe black alder woods. Criterion A • Centaurea donetzica Klokov; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Iris humilis Georgi (Iris pineicola Klokov); A(ii), A(iv); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • G1.414 Steppe swamp Alnus gluinosa woods; area: 300 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.A1 Quercus – Fraxinus – Carpinus betulus woodland on eutrophic and mesotrophic soils; area: 10000 ha; trend: stable; area data quality: good; trend data quality: good. • G3.4232 Sarmatic steppe Pinus sylvestris forests; area: 4750 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Бурда Р.І., Остапко В.М., Глухов А.З., Шпилева Н.В. Національний природний парк “Святі Гори”: біологічна різноманітність рослинного покриву // Заповідна справа в Україні. – 1997. – Т.3, вип. 1. – С. 10–17. 2. Дьякова О.В. Грабово-дубовий ліс в Національному природному парку “Святі Гори” // Менеджмент екосистем природно-заповідних територій. Мат-ли Всеукр. наук.-практ. конф., присвяч. 10-річчю створення Національного природного парку “Подільські Товтри”. – Кам’янець-Подільський: Аксіома, 2006. – С. 93–97. 3. Дьякова О.В. О нахождении Muscari neglectum Guss. на территории НПП “Святые Горы” // Промислова ботаніка: стан та перспективи розвитку: Мат-ли міжнар. наук. конф. “Промислова ботаніка: стан та перспективи розвитку” (Донецьк, 24–26 вересня 2007 р.). – Донецьк, 2007. – С.156–157. 4. Дьякова О.В. Рослинність вільхових лісів урочища Святогірський табір (НПП “Святі Гори”) // Відновлення порушених природних екосистем: Мат-ли Третьої міжнар. наук. конф. (м. Донецьк, 7–9 жовтня 2008 р.). – Донецьк, 2008. – С. 183–185. 5. Зацепина Д.Я., Хлевная Н.А. О флоре меловых обнажений заказника “Горы Артема” // Ботан. журн. – 1980. – 65, № 4. – С. 551–555. 6. Мальцева І.А. Грунтові водорості лісів національного природного парку “Святі Гори” (Донецька обл., Україна) // Мат-ли конф., присвяч. 80-річчю Канівського природного заповідника “Роль природно-заповідних територій у підтриманні біорізноманіття” (9–11 вересня 2003 р., м. Канів). – Канів, 2003. – С. 118–119. 7. Мальцева І.А., Супронюк І., Пушкіна О. Грунтові водорості крейдяних борів національного природного парку “Святі Гори” // 21–30 червня 2004 р., м. Дніпропетровськ). – Т. 31. Біологічні науки. – Дніпропетровськ: Наука і освіта, 2004. – 288 С. 35. 8. Морозова І. Міксоміцети Національного природного пароку “Святі Гори” // Матли ІV Міжн. наук. конф. студентів та аспірантів “Молодь і поступ біології” (м. Львів, 7–10 квітня 2008 р.). – Львів: ЛНУ ім. І. Франка, 2008. – С. 106–107. 9. Надєіна О.В. Лишайники національного природного парку “Святі Гори” // Чорноморський ботан. журн. – 2007. – 3, № 2. – С. 100–108. 10. Онищенко В.А., Дьякова О.В., Карпенко Ю.О. Лісова рослинність урочищ Теплинська Дача і Маяцька Дача (національний природний парк “Святі Гори”) // Чорноморський ботан. журн. – 2007. – 3, № 2. – С. 88–99. 11. Ордынец А.В., Акулов А.Ю. Предварительные данные о биоте афиллофороидных грибов Национального природного парка “Святые Горы” (Донецкая обл., Украина) // Актуальные проблемы Экологии и сохранения биоразнообразия. Сб. статей. – Владикавказ. – СОИТСИ, 2008. – С. 64–71. 12. Остапко В.М., Шпилева Н.В., Дьякова О.В. НПП Святі гори // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 440–456. 13. Тихоненко Ю.Я., Дудка І.О. Знахідки іржастих грибів (порядок Uredinales) в національному природному парку “Святі Гори” // Укр. ботан. журн. – 2005. – 62, № 4. – С. 495–499. 14. Трискиба С.Д., Полохіна І.І., Сухомлин М.М. Знахідка Grifola frondosa (Fr.) S. Gray на півночі Донецької області // Укр. ботан. журн. – 2005. – 62, № 9. – С. 87–90. 15. Устименко П.М., Попович С.Ю. Растительность проектируемого Славяногорского национального парка и зонирование его территории // Бюл. ботан. сада. – 1992. – Вып.164. – С.76–81. 16. Шпилевая Н.В. Синантропная флора национального природного парка “Святые Горы” // Відновлення порушених природних екосистем: мат-ли другої міжн. конф., 6–8 верес. 2005 р.: тезисы докл. – Донецьк: ТОВ “Лебідь”, 2005. – С. 109–110. 17. Шпилева Н.В. Оцінка антропогенної трансформації флори національного природного парку “Святі Гори” // Синантропізація рослинного покриву України: наук. конф.: тези. допов. – Київ, Переяслав-Хмельницький, 2006. – С. 220–223. Svydovets V.A. Onyshchenko Ukrainian name: Свидовець. Area: 21167.0 ha. Altitude: 570–1883 m. Latitude: 48°16’05” N (48.2681°). Longitude: 24°10’30” E (24.1749°). Administrative regions. Zakarpatska region: Tiachiv raion, Rakhiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.2%; D – 0.1%; E – 35.6%; F – 9.7%; G – 54.4%; H – 0.5%. Habitats. Level 2. C1 Surface standing waters – 0.0%; C2 Surface running waters – 0.2%; E4 Alpine and subalpine grasslands stands – 35.0%; E5 Woodland fringes and clearings and tall 289 forb stands – 0.6%; F2 Arctic, alpine and subalpine scrub – 9.7%; G1 Broadleaved deciduous woodland – 29.0%; G3 Coniferous woodland – 22.1%; G4 Mixed deciduous and coniferous woodland – 3.6%; H2 Screes – 0.0%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. C1.1 Permanent oligotrophic lakes, ponds and pools; C1.2 Permanent mesotrophic lakes, ponds and pools; C2.1 Springs, spring brooks and geysers; C2.2 Permanent non-tidal, fast, turbulent watercourses; E4.1 Vegetated snow-patch; E4.2 Moss and lichen dominated mountain summits, ridges and exposed slopes; E4.3 Acid alpine and subalpine grassland; E4.4 Calcareous alpine and subalpine grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; E5.5 Subalpine moist or wet tall-herb and fern stands; F2.2 Evergreen alpine and subalpine heath and scrub; F2.3 Subalpine deciduous scrub; F2.4 Conifer scrub close to the tree limit; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H2.4 Temperate-montane calcareous and ultra-basic screes; H3.1 Acid silicious inland clifs; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – major, forestry – minor, nature conservation and research – major, tourism/recreaion – minor. Protected areas: overlaps (8523 ha) with Karpatskyi biosphere reserve (naional category), overlaps (8523 ha) with Carpathian biosphere reserve (UNESCO), overlaps (8492 ha) with Emerald Site “Carpathian Biosphere Reserve”, overlaps (12644 ha) with Emerald Site “Zakhidnyi Svydovets”, overlaps (8670 ha) with World Heritage Site “Primeval Beech Forests of the Carpathians and the Ancient Beech Forests of Germany” (core zone: 3030.5 ha, bufer zone: 5639.5 ha). Threats: climate change/sea level rise – low, development (recreaion/tourism) – low. General description. One of the highest parts of the Ukrainian Carpathians. Large areas are occupied by the spruce forests, beech forests and the subalpine vegetaion. Picea abies forests prevail on the northeastern slope of the Svydovets Range. Upper limit of the forest vegetaion is formed by pure Picea abies forests. Typical dominants are Calamagrosis arundinacea, Luzula sylvaica, Vaccinium myrillus, Pleurozium schreberi, Polytrichum formosum. At lower alitudes, there are mixed forests dominated by Picea abies, Abies alba and Fagus sylvaica. Pure Fagus sylvaica forests occupy a large area on the southern slope. In the herb layer, there predominate Dentaria glandulosa (Cardamine glandulosa), Galium odoratum, Rubus hirtus. In the subalpine belt, signiicant areas are dominated by Juniperus sibirica, Duschekia alnobetula (Alnus alnobetula), Nardus stricta, Deschampsia cespitosa, Vaccinium myrillus, Calamagrosis villosa, Festuca airoides, Oreojuncus triidus (Juncus triidus). Someimes there dominate Festuca picta, Luzula alpinopininosa, Rhododendron myrifolium, Vaccinium uliginosum. In the wet habitats, there occur communiies of Adenostyles alliariae, Cirsium waldsteinii. Calcareous rocky grasslands dominated by Festuca inarmata (Festuca amethysina s.l.) or Festuca versicolor have small areas. Botanical significance. Important area for subalpine habitats and species, beech forests and oligotrophic aquaic habitats. Criterion A • Botrychium matricariifolium (A. Braun ex Döll) W.D.J.Koch; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Campanula abieina Griseb. & Schenk; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Hamatocaulis vernicosus (Mitt.) Hedenas (Drepanocladus vernicosus (Mitt.) Warnst.); A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Heterophyllium affine (Mitt.) Fleisch; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Narcissus angustifolius Curtis; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Neckera pennata Hedw.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Poa graniica Braun-Blanq. (Poa deylii Chrtek & V.Jirasek); A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion A • C1.1 Permanent oligotrophic lakes, ponds and pools; area: 2 ha; trend: decrasing; area data quality: medium; trend data quality: medium. • D2.226 Peri-Danubian black-white-star sedge fens; area: 3 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.11 Boreo-alpine acidocline snow-patch grassland and herb habitats; area: 10 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.12 Boreo-alpine calcicline snow-patch grassland and herb habitats; area: 1 ha; trend: stable; area data quality: poor; trend data quality: poor. • E4.3 Acid alpine and subalpine grassland; area: 7300 ha; trend: stable; area data quality: 290 291 poor; trend data quality: poor. E4.4 Calcareous alpine and subalpine grassland; area: 10 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.5 Subalpine moist or wet tall-herb and fern stands; area: 400 ha; trend: stable; area data quality: poor; trend data quality: poor. • F2.22 Alpide acidocline Rhododendron heaths; area: 30 ha; trend: stable; area data quality: poor; trend data quality: medium. • F4.2 Dry heaths; area: 10 ha; trend: stable; area data quality: poor; trend data quality: medium. • G1.12 Boreo-alpine riparian galleries; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. • G3.1B Alpine and Carpathian subalpine Picea forests; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.6 Fagus woodland; area: 5800 ha; trend: stable; area data quality: medium; trend data quality: medium. • H2.3 Temperate-montane acid siliceous screes; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. Conservaion proposals. Create an Emerald Sites including the enire IPA and a state reserve in the northwestern part of the IPA outside the Carpathian biosphere reserve. Literature 1.Бедей М.І. Близниці-Драгобрат (флора, рослинність, охорона). – Ужгород: Ліра, 2006. – 108 с. 2.Біорізноманіття Карпатського біосферного заповідника / Кол. авт., Ред. рада: Я.І. Мовчан, Ф.Д. Гамор та ін. – К.: Інтерекоцентр, 1997. – 711 с. 3.Гамор Ф.Д., Вайнагій І.В., Антосяк В.М. Стан охорони червонокнижних видів рослин на заповідних територіях Українських Карпат // Укр. ботан. журн. – 1994. – 51, № 5. – С. 122–129. 4.Гамор Ф.Д., Волощук М.І., Антосяк Т.М., Козурак А.В. БЗ Карпатський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 45–72. 5.Гамор Ф.Д., Довганич Я.О., Покиньчереда В.Ф. та ін. Праліси Закарпаття. Інвентаризація та менеджмент. – Рахів, 2008. – 86 с. 6.Малиновський К.А. Рослинність високогір’я Українських Карпат. – К.: Наук. думка, 1980.– 280 с. 7.Малиновський К.А., Крічфалушій В.В. Рослинні угруповання високогір’я Українських Карпат. – Ужгород, 2002. – 244 с. 8.Праліси в центрі Європи: Путівник по лісах Карпатського біосферного заповідника / Кол. авт., ред.: У-Б. Брендлі, Я. Довганич. – Бірменсдорф: Швейцарський федеральний ін-т досліджень лісу, снігу і ландшафтів (WSL) – Рахів: Карпатський біосферний заповідник (КБЗ), 2003. – 192 с. • Syra Pohonia V.A. Onyshchenko Ukrainian name: Сира Погоня. Area: 18811 ha. Altitude: 145–160 m. Latitude: 51°31’33” N (51.5258°). Longitude: 27°10’12” E (27.1699°). Administrative regions. Rivne region: Dubrovytsia raion (minor), Rokytne raion. Ownership: state, private (minor). Biogeographic regions: continental. Habitats. Level 1. D – 51%; G – 49%. Habitats. Level 2. D1 Raised and blanket bogs – 30%; D2 – Valley mires, poor fens and transition mires – 21%; G1 Broadleaved deciduous woodland – 10%; G3 Coniferous woodland – 28%; G4 Mixed deciduous and coniferous woodland – 11%. Futher habitat description. D1.1 Raised bogs; D2.3 Transition mires and quaking bogs; E1.7 Closed non-Mediterranean dry acid and neutral grassland; E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; G1.5 Broadleaved swamp 292 293 woodland on acid peat; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland, G4.1 Mixed swamp woodland, G4.4 Mixed Pinus sylvestris – Betula woodland. Land use: nature conservation and research – 100%. Protected areas: overlaps (9926 ha) with Rivnenskyi nature reserve, overlaps (9926 ha) with Emerald Site “Rivnenskyi Nature Reserve”. Threats: water (drainage) – low. General description. Raised bogs, Pinus sylvestris woods, and transiion mires. Dominants of the raised bogs are Eriophorum vaginatum, Sphagnum magellanicum, Sphagnum fuscum. Oten they have a sparse layer of Pinus sylvestris and Betula pubescens. In Sphagnum pine woods, typical dominants are Ledum palustre, Vaccinium uliginosum, Vaccinium oxycoccos (Oxycoccus palustris). In hollows, Sphagnum cuspidatum, Scheuchzeria palustris, Carex limosa, Carex rostrata dominate. Higher levels are occupied by Pinus sylvestris woods. Botanical significance. The largest raised bog in Ukraine. Criterion C • D2.3 Transition mires and quaking bogs; area: 3800 ha; trend: stable; area data quality: poor; trend data quality: medium. • G3.E Nemoral bog conifer woodland; area: 3000 ha; trend: stable; area data quality: medium; trend data quality: medium. • X04 Raised bog complexes; area: 7000 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Create a state reserve that will include the IPA outside Rivnenskyi nature reserve. Literature 1. Андрієнко Т.Л. ПЗ Рівненський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 313–324. 2. Андрієнко Т.Л., Прядко О.І., Онищенко В.А. Раритетна компонента флори Рівненського природного заповідника // Укр. ботан. журн. – 2006. – 63, № 2. – С. 220– 228. 3. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 215 с. 4. Водно-болотні угіддя України / під ред. Г.Б. Марушевського та І.С. Жарук. – К.: Чорноморська програма Ветландс Інтернешнл, 2006. – 312 с. 5. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Tarkhankut V.A. Onyshchenko Ukrainian name: Тарханкут. Area: 14379.0 ha. Altitude: 0–146 m. Latitude: 45°22’16” N (45.3711°). Longitude: 32°34’09” E (32.5692°). Administrative regions. Krym: Chornomorske raion; Territorial waters of Ukraine. 294 Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 21.9%; B – 0.01%; E – 69.2%; F – 1.0%; H – 0.9%; I – 7.0%; J – 0.05%. Habitats. Level 2. A2 Littoral sediment – 0.02%; A3 Infralittoral rock and other hard substrata – 15.0%; A4 Circalittoral rock and other hard substrata – 7.6%; A5 Sublittoral sediment – 0.2%; B1 Coastal dunes and sandy shores – 0.001%; B2 Coastal shingle – 0.002%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.01%; E1 Dry grasslands – 69.2%; F3 Temperate and mediterranean-montane scrub – 0.02%; F7 Spiny Mediterranean heaths – 0.9%; H1 Terrestrial underground caves, cave systems, passages and waterbodies, H2 Screes – 0.003%; H3 Inland cliffs, rock pavements and outcrops – 0.04%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.9%; I1 Arable land and market gardens – 7.0%; J2 Low density buildings – 0.01%; J3 Extractive industrial sites – 0.01%; J4 Transport networks and other constructed hard-surfaced areas – 0.03%. Futher habitat description. A2.1 Litoral coarse sediment; A2.2 Litoral sand and muddy sand; A2.4 Litoral mixed sediments; A2.5 Coastal saltmarshes and saline reedbeds; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.3 Atlanic and Mediterranean low energy infralitoral rock; A3.7 Features of infralitoral rock; A4.3 Atlanic 295 and Mediterranean low energy circalitoral rock; A5.1 Sublitoral coarse sediment; A5.2 Sublitoral sand; A5.4 Sublitoral mixed sediments; A5.5 Sublitoral macrophyte-dominated sediment; E1.1 Inland sand and rock with open vegetation, E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; F7.4 Hedgehog-heaths; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H3.5 Almost bare rock pavements, including limestone pavements; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resuling from recent ice acivity; H5.6 Trampled areas; I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – 30%; nature conservaion and research – 77%; tourism/ recreation – major. Protected areas: includes Charivna Havan naional nature park (10900 ha); includes Emerald Site “Charivna Havan’ Naional Nature Park” (10900 ha). Threats: development (recreation/tourism) – medium; eutrophicain – low. General description. The IPA includes areas occupied mainly by steppes on stony soils in the western part of the Crimean Peninsula and adjacent 1-km wide strip of the Black Sea. The shore is a popular place for sea diving. Dominants of marine vegetaion are Cladostephus spongiosus, Cystoseira crinita, Cystoseira barbata, Corallina elongata, Phyllophora crispa. Other typical species: Ceramium virgatum, Chondrophycus papillosus, Cladophora albida, Cladophora sericea, Dictyota fasciola, Dilophus fasciola, Laurencia coronopus, Laurencia obtusa, Ulva intesinalis, Ulva linza. Dry grasslands are dominated by: Agropyron pecinatum, Botriochloa ischaemum, Festuca rupicola, Festuca valesiaca, Koeleria brevis, Sipa capillata, Sipa lessingiana. Steppes of more xeric habitats difer by presence of Artemisia lerchiana, Artemisia taurica, Astragalus henningii, Centaurea orientalis, Dianthus capitatus, Galium ruthenicum, Linum tenuifolium, Medicago romanica, Scabiosa praemontana, Tanacetum paczoskii. Diferenial species of more mesic habitats are Ajuga salicifolia, Centaurea difusa, Filipendula vulgaris, Galium verum, Potenilla argentea, Salvia aethiopis, Salvia nemorosa, Salvia nutans, Veronica spicata. Artemisia-dominated steppes have been formed as a result of intensive grazing. Their dominants are Artemisia austriaca, Artemisia lerchiana, Artemisia taurica. Other important species of Artemisia-dominated steppes: Carthamus lanatus, Centaurea solsiialis, Euphorbia seguieriana, Salvia aethiopis, Sipa capillata, Sipa lessingiana. Diferenial species of Artemisia-dominated steppes on shallow rendzina soils are Artemisia lerchiana (dom.), Artemisia caucasica (dom.), Caragana scythica, Convolvulus cantabrica, Convolvulus holosericeus, Cota dubia (Anthemis dubia), Crambe aspera, Genista albida, Ononis pusilla, Teucrium chamaedrys, Teucrium polium, Veronica taurica. Typical species of abandoned arable lands are Centaurea difusa (dom.), Carduus nutans, Eryngium campestre, Euphorbia seguieriana, Euphorbia stepposa, Euphorbia virgata, Marrubium peregrinum, Salvia aethiopis. Tomillares are dominated by Thymus roegneri (Th. callieri), Th. dzevanovskyi, Asphodeline taurica, Jurinea stoechadifolia, Convolvulus holosericeus, Achillea nobilis with admixture (10–15%) of steppe species. Small areas are occupied by deciduous thickets and brushes (Berberis vulgaris, Coinus coggygria, Crataegus monogyna, Euonymus verrucosus, Genista albida, Hedera helix s.l., Jasminus fruicans, Malus sylvestris, Fraxinus excelsior, Prunus spinosa, Pyrus communis, Pyrus eleagnifolia, Rhamnus catharica, Rosa spp, Rubus sp. div., Ulmus minor; in the herb layer: Arum elongatum, Asparagus oicinalis, Asparagus litoralis, Asparagus vericillatus, Crambe mitridais, Dactylis glomerata, Malva erecta, Thalictrum minus. Botanical significance. One of the largest areas of steppe vegetaion and one of the most valuable sites of seaweed communiies in Ukraine. Criterion A • Centaurea taliewii Kleopow; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. • Crambe mitridais Juz.; A(iv); abundance: unknown; trend: unknown; species data quality: poor; trend data quality: poor. Criterion C • A3 Infralittoral rock and other hard substrata; area: 2000 ha; trend: stable; area data quality: medium; trend data quality: poor. • E1.2 Perennial calcareous grassland and basic steppes; area: 9800 ha; trend: increasing; area data quality: good; trend data quality: good. • F7 Spiny Mediterranean heaths; area: 100 ha; trend: unknown; area data quality: poor; trend data quality: poor. Conservaion proposals. Add coastal part of the sea to the Charivna Havan naional nature park and Emerald Site “Charivna Havan’ Naional Nature Park”. Literature 1. Белянина Н.Б., Шатко В.Г. Флористические находки с Тарханкутского полуострова // Бюл. Главн. ботанич. сада. – 1992. – Вып. 164. – С. 57–63. 2. Белянина Н.Б., Шатко В.Г. Конспект флоры Джангульского побережья (Крым) // Бюл. Главн. ботанич. сада. – 1999. – Вып. 178. – С. 43–65. 3. Голубева И.В., Маслова И.И. Оценка современного состояния и предложения по заповедной охране степной растительности в связи с организацией Тарханкутского заповедника // Фонды Никитс. ботан. сада. – Ялта, 1986. – 4 с. 4. Дідух Я.П., Вакаренко Л.П. Флористичні та ценотичні особливості Тарханкутського півострова (Крим) // Укр. ботан. журн. – 1987. – 44, № 3. – С. 31–36. 5. Маслов И.И. Фитобентос заповедной акватории “Прибрежный аквальный комплекс у мыса Атлеш” (Черное море) // Экология моря. – 2001. – Вып. 56. – С. 30–34. 6. Маслов И.И. Макрофитобентос некоторых заповедных акваторий Черного моря (Украина) // Альгология. – 2002. – 12, № 1 – С. 81–95. 7. Мильчакова Н.А. Макрофитобентос // Современное состояние биоразнообразия прибрежных вод Крыма (черноморский сектор). – Севастополь: ЭКОСИ-Гидрофизика, 2003. – С. 152–208. 8. Мільчакова Н.П., Вахрушева Л.П., Єпіхін Д.В. НПП Чарівна гавань // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 519–529. 9. Подгородецкий П.Д. Тарханкутский национальный природный парк // Заповедники Крыма – 2007. Мат-лы IV междунар. науч.-практ. конф., 2 нояб. 2007 г., Симферополь. – Ч. 1. Ботаника. Общие вопросы охраны природы. – Симферополь, 2007. – С. 341–352. 296 297 Habitats. Level 1. A – 75.0%; B – 0.3%; C – 1.8%; D – 2.0%; E – 20.8%; H – 0.1%. Habitats. Level 2. A2 Littoral sediment – 4.0%; A5 Sublittoral sediment – 71.0%; B1 Coastal dunes and sandy shores – 0.3%; B2 Coastal shingle – 0.1%; C1 Surface standing waters – 1.8%; D6 Inland saline and brackish marshes and reedbeds – 2.0%; E1 Dry grasslands – 1.5%; E2 – Mesic grasslands – 0.2%; E6 Inland salt steppes – 19.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.5 Coastal saltmarshes and saline reedbeds; A5.5 Sublitoral macrophyte-dominated sediment; B1.1 Sand beach driftlines; B1.2 Sand beaches above the driftline; B1.3 Shifting coastal dunes; B1.4 Coastal stable dune grassland (grey dunes); B1.8 Moist and wet dune slacks; B2.1 Shingle beach driftlines; B2.2 Unvegetated mobile shingle beaches above the driftline; C1.5 Permanent inland saline and brackish lakes, ponds and pools; D6.1 Inland saltmarshes; D6.2 Inland saline or brackish species-poor helophyte beds normally without free-standing water; E6.2 Continental inland salt steppes; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity. Land use: nature conservation and research – 85%. Protected areas: overlaps (about 44700 ha) with Chernomorskiy (Chornomorskyi, Black Sea) biosphere reserve (UNESCO, core zone of the reserve) and, Chornomorskyi biosphere reserve (naional category), overlaps (about 44700 ha) with Emerald Site “Black Sea Biosphere Reserve”. Threats: climate change/sea level rise – low. General description. The IPA includes Gulf of Tendra, smaller lagoons and salt lakes with adjacent inland salt marshes, salt steppes, accumulaive islands. Gulf of Tendra is up to 2.6 m depth. Its salinity is 15–18 ‰. Tendra island is a bar situated south to the gulf. It consists of sand and shells. Dominants of aquaic vegetaion are Zostera nolii (Nanozostera nolii), Zostera marina, Ruppia spiralis, Zannichellia maior, Potamogeton pecinatus (Stuckenia pecinata). On lower part of the beach Cakile maritima, Crambe pontica, Salsola kali subsp. pontica dominates. Typical species are Argusia sibirica, Lactuca tatarica, Xanthium albinum, Leymus sabulosus. On sand beaches above the dritline, dominants are Leymus sabulosus, Crambe pontica, Calamagrosis epigeios, Polygonum euxinum, Elytrigia bessarabica. Other typical species are Asparagus mariimus, Astrodaucus littoralis, Centaurea odessana, Cynanchum acutum, Eryngium mariimum, Lactuca tatarica, Polygonum mesembricum. Halophyic vegetaion is represented by the communiies of Juncus mariimus, Halocnemum strobilaceum, Salicornia perennans, Halocnemum strobilacеum, Frankenia pulverulenta, Lepidium pumilum, Puccinellia syvaschica, Puccinellia fomini, Puccinellia bilykiana, Puccinellia brachylepis (~ P. gigantea), Aeluropus litoralis, Bolbochoenus mariimus, Tripolium vulgare, Scirpus tabernaemontani. Drier salt habitats (salt steppes) are dominated by Artemisia santonica, Festuca valesiaca, Stipa capillata, Agropyron pectinatum, Elytrigia pseudocaesia. Typical species: Achillea setacea, Artemisia austriaca, Bromus mollis, Bromus squarrosus, Festuca pseudodalmatica, Festuca valesiaca, Halimione verrucifera, Limonium meyeri, Poa bulbosa, Dianthus guttatus, Milium vernale. Dominant species of dry grasslands on sands and shells (sand steppes) is Festuca beckeri, other typical species are Artemisia arenaria, Asperula setulosa, Centaurea odessana. In the mesic grasslands, there prevail Agrostis sabulicola, Calamagrosts epigeios, Cynodon dactylon, Elytrigia elongata, Elytrigia repens, Phleum phleoides, Poa angustifolia. Botanical significance. Important area for conservaion of sand steppes, litoral vegetaion, sand dunes, halophyic vegetaion, vegetaion of salt waters and endemic psammophyic and halophyic species. Criterion A • Allium regelianum A.Beckerex Iljin; A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. • Allium scythicum Zoz; A(iii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Alyssum borzaeanum Nyár. (Odontarrhena borzaeana (Nyár.) D.A.German); A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • A2.5 Coastal saltmarshes and saline reedbeds; area: 200 ha; trend: stable; area data quality: poor; trend data quality: medium. • A5 Sublitoral sediment; area: 37000 ha; trend: stable; area data quality: good; trend data quality: medium. • B1.3 Shifting coastal dunes; area: 50 ha; trend: stable; area data quality: medium; trend 298 299 Tendrivska Zatoka V.A. Onyshchenko, O.Yu. Umanets Ukrainian name: Тендрівська затока. Transliteraion/Translaion variants: Tendra Bay, Gulf of Tendra. Area: 52622.0 ha. Altitude: 0–3 m. Latitude: 46°14’48” N (46.2467°). Longitude: 31°54’11” E (31.9029°). Administrative regions. Kherson region: Hola Prystan raion; Territorial waters of Ukraine Ownership: state. Biogeographic regions: steppic. data quality: medium. B1.4 Coastal stable dune grassland (grey dunes); area: 50 ha; trend: stable; area data quality: medium; trend data quality: medium. • D6.1 Inland saltmarshes; area: 600 ha; trend: stable; area data quality: poor; trend data quality: medium. • E6.2 Continental inland salt steppes; area: 11150 ha; trend: stable; area data quality: poor; trend data quality: medium. Literature 1. Бiлик Г.I., Ткаченко В.С. Рослиннiсть урочища Потiївка Чорноморського державного заповiдника // Укр. ботан. журн. – 1970. – 27. № 4. – С. 491–496. 2. Войтюк Б.Ю., Уманець О.Ю., Соломаха І.В Синтаксономія галофільної рослинності Чорноморського біосферного заповідника // Науковий вісник Чернівецького ун-ту: Збірник наукових праць. – Вип. 193: Біологія. – Чернівці: Рута, 2004. – С. 85–92. 3. Мринський О.П. Рослиннiсть заповiдноi дiлянки Ягорлицького пiвострова / Охорона, вивчення та збагачення рослинного свiту. – Мiжвiдомчий збiрник. – К: Вища школа, 1975. – С. 41–44. 4. Ткаченко В.С., Лисенко Г.М., Маяцький Г.Б., Уманець О.Ю. Структурні зміни фітоценокомплексів Солоноозерної ділянки Чорноморського біосферного заповідника за даними періодичного картографування // Укр. ботан. журн. – 1997. – 54. № 3. – С. 232–239. 5. Ткаченко В.С., Маяцький Г.Б. Динамiка рослинностi Потiївськой дiлянки Чорноморського бiосферного заповiдника пiд впливом iригацiї // Укр. ботан. журн. – 1989. – 46. № 3. – С. 66–71. 6. Уманец О.Ю. Фитоценотическая характеристика сообществ с участием Puccinellia syvaschica Bilyk на территории Черноморского биосферного заповедника // Заповiдна справа в Українi. – 2000, Т.6. – Вип.1. – С. 14–16. 7. Уманець О.Ю. БЗ Чорноморський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 73–93. 8. Уманець О.Ю., Войтюк Б.Ю., Соломаха І.В. Синтаксономія рослинності Чорноморського біосферного заповідника. IV. Ділянка Потіївська // Укр. фітоцен. зб. – Київ, 2001. – 1 (17). – C. 66–86. 9. Уманець О.Ю., Соломаха I.В. Синтаксономiя рослинностi Чорноморського бiосферного заповiдника I. Урочище “Ягорлицький Кут” // Укр. фiтоцен. зб. – Київ. – 1998. – Сер. А., вип. 2 (11). – С. 109–127. 10. Уманець О.Ю., Соломаха І.В. Синтаксономія рослинності Чорноморського біосферного заповідника. II. Острів Тендра // Укр. фітоцен. зб. – Київ. – 1999, Сер.А, вип.1–2 (12–13). – C. 63–77. • Tepe-Oba V.A. Onyshchenko Ukrainian name: Тепе-Оба. Area: 3977.0 ha. Altitude: 0–287 m. Latitude: 45°00’09” N (45.0024°). 300 Longitude: 35°19’40” E (35.3276°). Administrative regions. Autonomous Republic of Crimea: Feodosia city; Territorial waters of Ukraine. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. A – 5.9%; B – 0.8%; E – 77.5%; F – 3.8%; G – 8.5%; H – 3.5%. Habitats. Level 2. A1 Littoral rock and other hard substrata – 0.1%; A2 Littoral sediment – 0.1%; A3 Infralittoral rock and other hard substrata sediment – 3.5%; A5 Sublittoral sediment – 2.2%; B2 Coastal shingle – 0.3%; B3 Rock cliffs, ledges and shores, including the supralittoral – 0.5%; E1 Dry grasslands – 76.5%; E6 Salt steppes – 1.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; F7 Spiny Mediterranean heaths – 1.8%; G1 Broadleaved deciduous woodland – 2.8%; G3 Coniferous woodland – 5.7%; H2 Screes – 0.5%; H3 Inland clifs, rock pavements and outcrops – 2.9%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. A2.1 Litoral coarse sediment; A2.5 Coastal saltmarshes and saline reedbeds; A3.2 Atlanic and Mediterranean moderate energy infralitoral rock; A3.2 Atlanic and Mediterranean low energy infralitoral rock; A5.1 Sublitoral coarse sediment; A5.5 Sublitoral macrophyte-dominated sediment; B2.1 Shingle beach dritlines; B2.2 Unvegetated mobile shingle beaches above the dritline; B2.3 Upper shingle beaches with open vegetaion; B3.1 Supralitoral rock (lichen or splash zone); B3.2 Unvegetated rock clifs, ledges, shores and islets; B3.3 Rock clifs, ledges and shores, with angiosperms; B3.4 Sot sea-clifs, oten vegetated; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E1.3 Mediterranean xeric grassland; F3.2 Submediterranean deciduous thickets and brushes; F7.4 Hedgehog-heaths; F9.3 Southern riparian galleries and thickets; G1.7 Thermophilous deciduous woodland; G3.F Highly 301 ariicial coniferous forestry plantations; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: agriculture (animals) – major, tourism/recreaion – minor Protected areas: includes Tepe-Oba regional botanical reserve (1200 ha), overlaps with Tykha Bukta regional landscape park (about 1499 ha), same as Emerald Site “Tepe-Oba”. Threats: development (recreaion/tourism) – medium, eutrophicaion – medium. General description. Tepe-Oba is the easternmost part of the Crimean mountains with alitudes up to 238 m over the sea level. Major vegetaion type is the steppe. Besides there are signiicant areas of sparsely vegetated rocks and screes, dry open rock debris swards, grasslands of submediterranean type with high cover of annuals, woods of Quercus pubescens, forest plantaions of Pinus. Slope to the sea is steep, with clifs about 100 m high. Shore consists of rocks, boulders, pebble and gravel. Dominant macrophytes in the sea are Cystoseira crinita, Cystoseira barbata, Polisiphonia elongata. Botanical significance. Important area for conservaion of dry grasslands, sea and inland clifs, marine macrophytes communiies, threatened endemic rock and steppe species. • Astracantha arnacantha (M.Bieb.) Podlech; A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Astragalus reduncus Pall.; A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe aspera M. Bieb.; A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe koktebelica (Junge) N.Busch; A(ii); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Crambe steveniana Rupr.; A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Lepidium turczaninowii Lipsky; A(i), A(ii), A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Onobrychis pallasii (Willd.) M.Bieb.; A(iii); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. • Ophrys oestrifera Bieb.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Orchis punctulata Steven ex Lindl.; A(ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Stipa syreistschikowii P.Smirn.; A(ii), A(iv); abundance: unknown; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • A3 Infralittoral rock and other hard substrata; area: 150 ha; trend: decreasing; area data quality: medium; trend data quality: poor. • B3.3 Rock cliffs, ledges and shores, with angiosperms; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. • E1.2 Perennial calcareous grassland and basic steppes; area: 700 ha; trend: stable; area data quality: medium; trend data quality: medium. • F7 Spiny Mediterranean heaths; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. • H3.2 Basic and ultra-basic inland cliffs; area: 40 ha; trend: stable; area data quality: poor; trend data quality: medium. 302 Literature 1. Костенко Н.С., Дикий Е.А., Алексеева Н.А. Донная растительность Юго– Восточного Крыма // Сборник научных трудов, посвященных 90–летию Карадагской научной станции и 25–летию Карадагского природного заповедника НАН Украины. – Симферополь: СОНАТ, 2004. – С. 66–84. 2. Костенко Н.С., Дикий Е.А., Заклецкий А.А., Марченко В.С. Донная растительность приоритетных акваторий юго-восточного Крыма: современное состояние и необходимые меры по сохранению // Заповедники Крыма – 2007. – Симферополь, 2007. – С. 63–68. 3. Шатко В.Г., Миронова Л.П. Конспект флоры хребта Тепе-Оба (Крым) // Бюллетень Главного ботанического сада. – 2011. – Вып. 197. – С. 43–70. Ternava – Dnister V.A. Onyshchenko Ukrainian name: Тернава – Дністер. Area: 1601.0 ha. Altitude: 122–260 m. Latitude: 48°36’35” N (48.6097°). Longitude: 26°47’30” E (26.7917°). Administrative regions. Chernivtsi region: Kelmentsi raion; Kmelnytskyi region: KamianetsPodilskyi raion. Ownership: state (major), private. Biogeographic regions: coninental. Habitats. Level 1. C – 10.9%; E – 24.8%; F – 2.9%; G – 59.5%; H – 1.9%. Habitats. Level 2. C1 Surface standing waters – 10.9%; E1 Dry grasslands – 24.8%; F3 Temperate and mediterranean-montane scrub – 2.9%; G1 Broadleaved deciduous woodland – 59.5%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 1.8%. Futher habitat descripion. C1.2 Permanent mesotrophic lakes, ponds and pools; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs. Land use: agriculture (animals) – major, forestry – major, nature conservation and research – major, tourism/recreaion – minor. Protected areas: overlaps (774 ha) with Podilski Tovtry naional nature park, overlaps (662 ha) with Khotynskyi naional nature park, includes Kytaihorodske Vidslonennia state geological nature monument (60 ha), includes Chaplia state botanical reserve (177 ha), overlaps (774 ha) with Emerald Site “Podilski Tovtry Naional Nature Park”, overlaps (662 ha) with Emerald Site “Khotynskyi Naional Nature Park”. Threats: agricultural intensification/expansion (grazing) – low, development (recreaion/ tourism) – low. General description. Steep slopes of the Ternava and Dnister rivers with dry grasslands, limestone and sandstone rocks, shrub vegetaion and woods. Steppe vegetaion is dominated by Carex humilis, Festuca valesiaca, Sesleria heuleriana, Sipa capillata, 303 Botriochloa ischaemum, Koeleria cristata, Potenilla incana. Typical species are Asperula cynanchica, Campanula sibirica, Filipendula vulgaris, Galium verum, Medicago falcata, Salvia vericillata, Scabiosa ochroleuca, Silene eugeniae, Teucrium chamaedrys, Thymus marschallianus. Shrub vegetaion is represented mainly by Prunus spinosa communiies. Besides there are Crataegus curvisepala, C. fallacina, C. monogyna, Cerasus mahaleb, Prunus stepposa, Swida sanguinea (Cornus sanguinea). The tree layer of woods consists of Quercus robur, Quercus petraea, Sorbus torminalis. In the shrub layer, there occur Cornus mas, Staphylea pinnata, Viburnum lantana. On the outcrops, there are Allium montanum, Asplenium ruta-muraria, Aurinia saxailis, Cleistogenes bulgarica, Poa versicolor, Sedum acre, Sedum sexangulare. Botanical significance. Important area for conservaion of Podolian steppes, shrubs and rocks and several endemic species. 304 Criterion A • Aconitum besserianum Andrz.; A(iiі); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Iris hungarica Waldst. & Kit.; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. • Schivereckia podolica Andrz. ex DC. (Draba podolica (Besser) Rupr.); A(ii); abundance: occasional (1000 individuals); trend: stable; species data quality: good; trend data quality: medium. • Spiraea polonica Błocki; A(iii); abundance: rare; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.11 Euro-Siberian rock debris swards; area: 15 ha; trend: stable; area data quality: medium; trend data quality: good. • E1.2 Perennial calcareous grassland and basic steppes; area: 370 ha; trend: stable; area data quality: medium; trend data quality: medium • F3.247 Ponto-Sarmatic deciduous thickets; area: 40 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.7 Thermophilous deciduous woodland; area: 100 ha; trend: stable; area data quality: poor; trend data quality: poor. • H2.6 Calcareous and ultra-basic screes of warm exposures; area: 1 ha; trend: stable; area data quality: medium; trend data quality: good. • H3.2 Basic and ultra-basic inland cliffs; area: 25 ha; trend: stable; area data quality: poor; trend data quality: good. Literature 1. Волуца О.Д. Spiraea polonica Błocki (Rosaceae) у Чернівецькій області // Актуальні проблеми ботаніки та екології. Матеріали міжнародної конверенції молодих учених. Кременець. 11-15 серпня 2009 р. – Тернопіль, 209. – С. 61-62. 2. Волуца О.Д., Токарюк А.І., Чорней І.І., Буджак В.В. Раритетні види флори національного природного парку “Хотинський”: поширення, ценотична приуроченість // Прагматичні аспекти діяльності національних природних парків у контексті збалансованого розвитку : матеріали міжнар.-практ. конф., присвяч. 20-річчю нац. природ. парку “Вижницький” (17-19 вер. 2015 р., смт Берегомет, Чернівецька обл., Україна). – Чернівці: ДрукАрт, 2015. – С. 326–347. 3. Волуца О. Д., Чорней І. І. Родина Зозулинцеві у флорі Північної Бессарабії // Запов. справа в Україні. – 2009. – Т. 15, вип. 2. – С. 26–31. 4. Заповідні перлини Хмельниччини / під ред. Т.Л.Андрієнко. – Хмельницький: ПАВФ “Інтрада”, 2006. – 220 с. 5. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 6. Федорончук М. М., Белемець Н. М., Волуца О. Д. Рідкісні види роду Spiraea L. (Rosaceae) флори України та стан їхньої охорони // Укр. ботан. журн. – 2013. – 70, № 2. – С. 164–167. 7. Чорней І. І., Буджак В. В., Токарюк А. І. Сторінками Червоної книги України (рослиннийсвіт). Чернівецька область. – Чернівці: ДрукАрт, 2010. – 452 с. 305 Tiup-Tarkhan i Kalynivskyi Pivostriv V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Тюп-Тархан і Калинівський півострів. Transliteraion/Translaion variants: Tiup-Tarkhan and Kalynivskyi Peninsula. Area: 5266.0 ha. Altitude: 0–4 m. Latitude: 45°48’07” N (45.8018°). Longitude: 34°40’40” E (34.6778°). Administrative regions. Autonomous Republic of Crimea: Dzhankoi raion. Ownership: state. Biogeographic regions: steppic. “Eastern Syvash” (4050 ha). Threats: natural events: erosion – low. General description. A part of shores of the Eastern Syvash with the steppe and halophyic vegetaion. The steppes are dominated by Agropyron pectinatum, Artemisia santonica, Carex melanostachya, Festuca valesiaca, Kochia prostrata, Poa bulbosa, Sipa capillata, S. ucrainica. Other frequent species are Atriplex aucheri, Elisanthe viscosa, Limonium tschurjukiense, Phlomis pungens, Verbascum densilorum. Mesic grasslands are dominated by Elytrigia elongata and E. repens. Dominants of salt grasslands are Argusia sibirica, Artemisia santonica, Salsola soda (Soda inermis), Tripolium pannonicum. The litoral halophyic vegetaion is formed mainly by Halocnemum strobilaceum, Halimione verrucifera, Salicornia perennans, Puccinellia fominii, Aeluropus litoralis. Botanical significance. One of the best sites for endemic species Limonium tschurjukiense. Criterion A • Limonium tschurjukiense (Klokov) Lavrenko ex Klokov; A(iv); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. Conservaion proposals. Сreate Syvaskyi national nature park and an Emerald Site including the enire IPA. Literature 1. Коломійчук В. П., Онищенко В. А., Перегрим М. М. Важливі ботанічні території Приазов’я / за ред. Т. Л. Андрієнко. – К. : Альтерпрес, 2012. – 114 с. 2. Котов С.Ф., Вахрушева Л.П. Растительный покров Калиновского регионального ландшафтного парка (современное состояние и перспективы сохранения ценогенофонда) // Бюлл. Никитск. ботан. сада, 2003. – Вып. 88. – С. 34–37. 3. Котов С.Ф., Вахрушева Л.П., Бирюлева Э.Г. Научное обоснование о целесообразности организации в Крыму государственного ботанического заказника “Калиновский”. – Симферополь: Экоцентр “Синтез НТ”, 1991. – 21 с. Tovtrivska Sinka Habitats. Level 1. A – 62.8%; E – 37.2%. Habitats. Level 2. A2 Littoral sediment – 61.8%; A5 Sublittoral sediment – 1.0%; E1 Dry grasslands – 11.4%; E6 Salt steppes – 25.8%. Futher habitat description. A2.3 Littoral mud; A2.4 Littoral mixed sediments; A2.5 Coastal saltmarshes and saline reedbeds; A5.3 Subittoral mud; E1.2 Perennial calcareous grassland and basic steppes; D6.1 Inland saltmarshes; E6.2 Continental inland salt steppes. Land use: agriculture (animals) – major; nature conservaion and research – major. Protected areas: overlaps (about 3300 ha) with Kalynivskyi regional landscape park, overlaps (about 3700 ha) with Ramsar Site “Eastern Syvash”, overlaps with Emerald Site I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Товтрівська стінка. Transliteraion/Translaion variants: Tovtry Wall, Tovtry Clif. Area: 16.1 ha. Altitude: 196–255 m. Latitude: 48°33’51” N (48.5642°). Longitude: 25°52’03” E (25.8675°). Administrative regions. Chernivtsi region: Zastavna raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1: E – 89.0%, F – 1.0%; H – 10.0% . Habitats. Level 2: E1 Dry grasslands – 89.0%; F3 Temperate and mediterranean-montane scrub – 1.0%; H3 Inland cliffs, rock pavements and outcrops – 10.0%. Futher habitat description: E1.1 Inland sand and rock with open vegetaion; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; H3.2 Basic and ultra-basic inland clifs. Land use: nature conservation and research – major. 306 307 Protected areas: includes Tovtrivska Sinka state botanical reserve . Threats: –. Triokhizbenskyi Step V.A. Onyshchenko Ukrainian name: Трьохізбенський степ. Transliteraion/Translaion variants: Triokhizbens’kyi Steppe. Area: 3281.0 ha. Altitude: 50–150 m. Latitude: 48°48’37” N (48.8103°). Longitude: 38°57’59” E (38.9664°). Administrative regions. Luhansk region: Slovianoserbsk raion, Novoaidar raion. Ownership: state. Biogeographic regions: steppic. General description. Dry grasslands, gypsum and limestone outcrops. Grasslands are dominated by Carex humilis, C. montana, Festuca valesiaca, Koeleria cristata, Poa angustifolia, Sesleria heufleriana, Stipa capillata, S. pennata. Other frequent species are Achillea submillefolium, Asperula cynanchica, Astragalus austriacus, A. onobrychis, Anthericum ramosum, Bupleurum falcatum, Galium verum, Gypsophila thyraica, Minuartia thyraica, Potentilla arenaria, Salvia pratensis, S. verticillata, Securigera varia, Teucrium chamaedrys, T. pannonicum, Thymus marschallianus, Trifolium montanum. Botanical significance. Large populaion of endemic species Gypsophila thyraica. Criterion A • Gypsophila thyraica A.Krasnova; A(iiі); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Literature 1. Чорней І.І., Скільський І.В., Коржик В.П., Буджак В.В. Заповідні об’єкти Буковини загальнодержавного значення як основа регіональної екологічної мережі // Заповідна справа в Україні. – 2001. – Т. 7, вип. 2. – С. 73–98. 308 Habitats. Level 1. E – 81.0%; F – 2.0%; G – 16.0%; H – 1.0%. Habitats. Level 2. E1 Dry grasslands – 76.0%; E3 Seasonly wet and wet grasslands – 5.0%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 8.0%; G3 Coniferous woodland – 8.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland (× E1.1); E3.4 Moist or wet eutrophic and mesotrophic grassland; F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland; G3.4 Pinus sylvestris woodland south of the taiga; H5.3 Sparsely- or un-vegetated habitats 309 on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: nature conservaion and research – 100%. Protected areas: included in Luhanskyi nature reserve (same as Triokhizbenskyi Step division of the reserve), included in Emerald Site “Luhanskyi Nature Reserve”. Threats: abandonment/reducion of land management – low. General description. A part of sand terrace over the loodplain of the Siverskyi Donets river. Prevailng vegetaion is open grasslands on sand dominated by Koeleria sabuletorum, Festuca beckeri, Sipa borysthenica, Carex colchica, Agropyron tanaiicum, Agropyron lavrenkoanum, Calamagrosis epigeios, Artemisia marschalliana. These habitats are rich in endemic species (Achillea micrantha, Agropyron tanaiicum, Anchusa popovii, Astragalus varius, Centaurea majorovii, Jacobaea borysthenica (Senecio borysthenicus), Jurinea thyrsilora, Linaria dulcis, Linaria genisifolia, Tragopogon tanaiicus, Tragopogon ucrainicus). Besides there are wet meadows (Juncus ariculatus, Juncus conglomeratus), shrub communiies (Salix acuifolia, Salix rosmarinifolia), woods (Betula pendula, Populus tremula, Populus nigra, Alnus gluinosa, Pinus sylvestris). Botanical significance. Important area for conservaion of sand steppes and endemic psammophyic species. Criterion A • Allium savranicum Besser; A(ii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E1.9 Open non-Mediterranean dry acid and neutral grassland, including inland dune grassland; area: 2400 ha; trend: stable; area data quality: medium; trend data quality: medium. • X35 Inland Sand Dunes; area: 300 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Русіна Н.В., Ходосовцев О.Є. Ліхенобіота Трьохізбенського полігону як перспективного відділення Луганського природного заповідника // Наукові праці Луганського природного заповідника. Рослинний і тваринний світ та його охорона. – Луганськ. – 2008. – Вип. 1, присвячений 40-річному ювілею Луганського природного заповідника. – С. 38–43. 2. Русіна Н.В. Історія та сучасний стан дослідження ліхенобіоти Луганського природного заповідника // Наукові праці Луганського природного заповідника. Рослинний і тваринний світ та його охорона. – Луганськ. – 2011. – Вип. 2. – С. 47–53 3. Сова Т.В., Боровик Л.П. ПЗ Луганський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 221–253. 4. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 310 Troitska Balka V.P. Kolomiychuk, V.A. Onyshchenko Ukrainian name: Троїцька балка. Transliteraion/Translaion variants: Troits’ka Ravine. Area: 387.0 ha. Altitude: 25–81 m. Latitude: 47°04’07” N (47.0685°). Longitude: 35°26’35” E (35.4430°). Administrative regions. Zaporizhia region: Melitopol raion Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. E – 82.3%; F – 0.1%; G – 15.4%; H – 1.8%; J – 0.4%. Habitats. Level 2. E1 Dry grasslands – 81.3%; E2 Mesic grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 0.1%; G1 Broadleaved deciduous woodland – 15.4%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.8%; J4 Transport networks and other constructed hard-surfaced areas – 0.4%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; G1.C Highly artificial broadleaved deciduous forestry plantations; H5.6 Trampled areas; J4.3 Rail networks. Land use: agriculture (animals) – major; forestry – major; nature conservaion and research – minor; urban/industrial/transport – minor. Protected areas: includes regional entomological reserve “Tsilynna balka Troitska, dilianka №1” (17 ha), includes regional entomological reserve “Tsilynna balka Troitska, dilianka №2” (9 ha), includes regional botanical reserve reserve “Troitska balka” (1 ha), included in Emerald Site “Troitska Balka”. 311 Threats: forestry (aforestaion) – medium, included in Emerald Site “Troitska Balka”. General description. A valley with prevailing steppe vegetaion dominated by Sipa lessingiana, Sipa capillata, Sipa ucrainica, Agropyron pecinatum, Festuca valesiaca. Botanical significance. Important area for threatened steppe species Calophaca wolgarica, Tulipa ophiophylla, Cymbochasma borysthenica, Allium pervestitum, Elytrigia stipifolia, Caragana scythica, Centaurea talievii, Astragalus pallescens, Eremogone rigida, Dianthus palidilorus. Criterion A • Calophaca wolgarica (L.f.) DC.; A(iv); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Conservaion proposals. Do not allow ariicial aforestaion. Сreate a state botanical reserve and an Emerald Site including the enire IPA. Literature 1. Коломійчук В.П. Ключові ботанічні території Північного Приазов’я // Заповідна справа в Україні. – 2008. – Т.14, вип. 1. – С. 61–66. 2. Коломійчук В. П., Онищенко В. А., Перегрим М. М. Важливі ботанічні території Приазов’я / за ред. Т. Л. Андрієнко. – К. : Альтерпрес, 2012. – 114 с. occupies the largest area. Besides there are termophilous Quercus robur forests, ariicial plantaions of coniferous and broadleaved trees, outcrops of limestone, mesic meadows and reed marshes. Trosianets V.A. Onyshchenko, O.M. Popova Ukrainian name: Тростянець. Area: 665.0 ha. Altitude: 40–150 m. Latitude: 47°29’05” N (47.4847°). Longitude: 29°11’50” E (29.1973°). Administrative regions. Odesa region: Krasni Okny raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 1.6%; E – 70.9%; F – 2.0%; G – 24.0%; H – 1.5%. Habitats. Level 2. C3 Littoral zone of inland surface waterbodies – 1.6%; E1 Dry grasslands – 69.0%; E2 Mesic grasslands – 1.9%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 12.0%; G3 Coniferous woodland – 12.0%; H2 Screes – 0.2%; H3 Inland cliffs, rock pavements and outcrops – 1.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; E2.5 Meadows of the steppe zone; F3.2 Submediterranean deciduous thickets and brushes; G1.7 Thermophilous deciduous woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity; H5.6 Trampled areas. Land use: agriculture (animals) – 70%; forestry – 24%; mowing/hay making – minor. Protected areas: same as Emerald Site “Trosianetskyi”. Threats: abandonment/reducion of land management – low; agricultural intensiicaion/ expansion (grazing) – low; forestry (aforestaion) – low. General description. Valleys of the Trosianets river and its tributaries. The steppe vegetaion 312 Botanical significance. One of two localiies of Genista tetragona in Ukraine. Criterion A • Genista tetragona Besser; A(i), A(ii), A(iv); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Сreate a state botanical reserve and an Emerald Site including the enire IPA. 313 Tsetsyno I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Цецино. Area: 519 ha. Altitude: 295–537 m. Latitude: 48°18’07” N (48.3019°). Longitude: 25°49’45” E (25.8292°). Administrative regions. Chernivtsi region: Chernivtsi city, Kitsman raion, Storozhynets raion. Ownership: state. Biogeographic regions: coninental. avellana, Swida sanguinea (Cornus sanguinea), Viburnum opulus, rarely Staphylea pinnata. Frequent summer species of the herb layer are Galium odoratum, Lamium galeobdolon, Pulmonaria obscura, Asarum europaeum, Mercurialis perennis, Aegopodium podagraria, Actaea spicata, Dryopteris ilix-mas, Salvia gluinosa, Symphytum cordatum, Paris quadrifolia, Stachys sylvaica. Spring ephemeroids are respresented by Allium ursinum, Corydalis cava, Corydalis solida, Crocus heuffelianus, Ficaria verna, Isopyrum thalictroides. Typical are calciphilous species Cephalanthera damasonium, C. longifolia, C. rubra, Cypripedium calceolus, Epipactis helleborine, Epipactis purpurata, Neottia nidus-avis, Platanthera bifolia, Sorbus torminalis, Taxus baccata. Botanical significance. Important area for calciphilous beech forests and Cypripedium calceolus. Criterion A • Cypripedium calceolus; A(ii); abundance: occasional; trend: unknown; species data quality: good; trend data quality: poor. Criterion C • G1.66 Medio-European limestone Fagus forests (*9150); area: 300 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Чорней І.І., Скільський І.В., Коржик В.П., Буджак В.В. Заповідні об’єкти Буковини загальнодержавного значення як основа регіональної екологічної мережі // Заповідна справа в Україні. – 2001. – Т. 7, вип. 2. – С. 73–98. Tulyntsi – Makedony Habitats. Level 1: G – 99.2%, H – 0.2%, J – 0.6%. Habitats. Level 2: G1 Broadleaved deciduous woodland – 99.2%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%, J4 Transport networks and other constructed hard-surfaced areas – 0.6%. Futher habitat description: G1.6 Fagus woodland; H5.6 Trampled areas, J4.2 Road networks. Land use: forestry – minor; nature conservation and research – major. Protected areas: included in Chernivetskyi regional landscape park, include Tsetsyno state landscape reserve (430 ha), included in Emerald Site “Chernivetskyi Regional Landscape Park”. Threats: forestry (intensiied forest management) – low. General description. Fagus sylvaica forest with paricipaion of Acer platanoides and Acer pseudoplatanus. Sparse shrub layer consists Sambucus nigra (predominantly), Corylus V.A. Onyshchenko Ukrainian name: Тулинці – Македони. Area: 529.0 ha. Altitude: 114–182 m. Latitude: 49°48’49” N (49.8135°). Longitude: 31°08’18” E (31.1383°). Administrative regions. Kyiv region: Myronivka raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 75.1%; F – 0.1%; G – 24.2%; H – 0.6%. Habitats. Level 2. E1 Dry grasslands – 70.1%; E2 Mesic grasslands – 5.0%; F3 Temperate and mediterranean-montane scrub – 0.1%; G1 Broadleaved deciduous woodland – 24.2%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.6%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Land use: agriculture (animals) – major; nature conservaion and research – minor. Protected areas: includes regional botanical reserve “Tulynetski Perelisky” (88 ha). Threats: agricultural intensification/expansion (grazing) – medium. General description. Valleys with the steppe and forest vegetaion. Major dominants of grasslands are Poa angusifolia, Bromopsis inermis, Botriochloa ischaemum, Calamagrosis epigeios. Communiies with the dominance of Carex humilis, Festuca rupicola, Festuca valesiava, Sipa capillata, Sipa pennata occupy smaller areas. Frequent species are Carex 314 315 praecox, Elytrigia intermedia, Elytrigia repens, Medicago falcata, Salvia pratensis. The grasslands have many species that are character species of meadows steppes: Adonis vernalis, Anemone sylvestris, Astragalus onobrychis, Astragalus dasyanthus, Bulbocodium versicolor, Crocus reiculatus, Dianthus membranaceus, Friillaria ruthenica, Inula hirta, Iris hungarica, Jurinea arachnoidea, Jurinea salicifolia, Jurinea calcarea, Hyacinthella leucophaea, Pedicularis kaufmannii, Pulsailla pratensis, Salvia nemorosa, Scorzonera purpurea, Thalictrum minus. In botoms of the valleys there are mesic and wet meadows. Turova Dacha V.A. Onyshchenko, N.V. Shumska Ukrainian name: Турова дача. Area: 1046.0 ha. Altitude: 402–420 m. Latitude: 48°52’02” N (48.8672°). Longitude: 24°14’36” E (24.2433°). Administrative regions. Ivano-Frankivsk region: Rozhniaiv raion. Botanical significance. One of the largest areas of meadow steppes in Ukraine. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 350 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Бортняк М.М., Войтюк Ю.О., Любченко В.М., Голяченко Т.В. Флористичні особливості ділянки ділянки степу Шандра-Тулинці // Укр. ботан. журн. – 1993. – 50, № 2. – С. 122–125. 2. Василюк О., Костюшин В., Норенко А., Плига А., Прекрасна Є., Коломицев Г., Фатікова М. Природно-заповідний фонд Київської області. Київ: НЕЦУ, 2012. – 338 с. 3. Кучерява Л. Ф., Шевчик В. Л., Бакаліна М. В., Тищенко О. В. Червонокнижні види у заказнику “Тулинецькі переліски” (Київська обл.) // Роль природно-заповідних територій у підтриманні біорізноманіття. Матеріали конф. – Канів, 2003. – С. 116. 4. Кучерява Л. Ф., Шевчик В. Л., Тищенко О. В. Судинні рослини заказника “Тулинецькі переліски” (Київська обл.) // Заповідна справа в Україні. – 2007. – 13, 1–2. – С. 38–41. 5. Мельник В. І., Гриценко В. В. Росслинний покрив урочища “Тулинецькі переліски” – еталон лучних степв Київського плато // Збірник наукових праць Полтавського дер. пед. ун-ту ім. В. Г. Короленка. Серія “Екологія.Біологічні науки”. – Полтава, 2005. – №4 (43) – С. 22–28. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. C – 0.0%; D – 0.3%; E – 0.1%, G – 98.9%; H – 0.7%. Habitats. Level 2. C2 Surface running waters – 0.0%; D1 Raised and blanket bogs – 0.2%; D2 Valley mires, poor fens and transition mires – 0.1%; E3 Seasonally wet and wet grasslands – 0.1%; G1 Broadleaved deciduous woodland – 5.5%; G3 Coniferous woodland – 73.4%; G4 Mixed deciduous and coniferous woodland – 20.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.7%. Futher habitat description. C2.3 Permanent non-tidal, smooth-flowing watercourses; D1.1 Raised bogs; D2.2 Poor fens and sot-water spring mires; D2.3 Transiion mires and quaking bogs; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.5 Broadleaved swamp woodland on acid peat; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus 316 317 aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G3.E Nemoral bog conifer woodland; G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland. Land use: forestry – major, nature conservation and research – 24%. Protected areas: includes state hydrological reserve “Turova Dacha” (255 ha), included in Emerald Site “Turova Dacha”. Threats: burning of vegetaion – low, eutrophicaion – low; water (drainage) – low. General description. Swamped Pinus sylvestris woods with the layer of Sphagnum and wet Pinus sylvestris woods. In the layer of herbs and small shrubs of the swamped woods, there dominate Eriophorum vaginatum, Ledum palustre, Vaccinium oxycoccos (Oxycoccus palustris), Vaccinium uliginosum. The moss layer is formed by Sphagnum capillifolium, S. magellanicum, S. recurvum s.l., Polytrichum strictum. In the forests of lower moisture, typical dominant is Vaccinium myrillus. The area of swamped woods is decreasing because of drainage works carried out several decades ago. Botanical significance. The largest Sphagnum pine wood in the alpine biogeographic region of Ukraine. Criterion C • G3.E Nemoral bog conifer woodland; area: 100 ha; trend: decreasing; area data quality: poor; trend data quality: good. Conservaion proposals. Increase the groudwater level. Literature 1. Онищенко В.А., Андрієнко Т.Л. Клас Oxycocco-Sphagnetea Br.-Bl. et Tüxen ex Westhoff et al. 1946 в Українських Карпатах. – Укр. ботан. журн. – 2015. – 72 (3). – С. 218–228. 2. Природно-заповідні території та об’єкти Івано-Франківщини. – Івано-Франківськ, 2000. – 272 с. Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; D1.1 Raised bogs; D2.2 Poor fens and sot-water spring mires; D2.3 Transiion mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.1 Inland sand and rock with open vegetation; E3.4 Moist or wet eutrophic and mesotrophic grassland; F9.1 Riverine scrub; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.5 Broadleaved swamp woodland on acid peat; G1.8 Acidophilous Quercus-dominated woodland; G1.9 Nonriverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga (major); G3.E Nemoral bog conifer woodland; G4.1 Mixed swamp woodland; G4.4 Mixed Pinus sylvestris – Betula woodland. Ubort – Bolotnytsia V.A. Onyshchenko Ukrainian name: Уборть – Болотниця. Area: 23423 ha. Altitude: 148–178 m. Latitude: 51°30’40” N (51.5111°). Longitude: 27°57’03” E (27.9508°). Administrative regions. Zhytomyr region: Olevsk raion, Ovruch raion. Ownership: state Biogeographic regions: coninental. Habitats. Level 1. C – 0.2%; D – 11.0%; E – 1.4%; F – 1.0%; G – 85.4%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.04%; C2 Surface running waters – 0.03%; C3 Littoral zone of inland surface waterbodies – 0.13%; D1 Raised and blanket bogs – 1%; D2 Valley mires, poor fens and transition mires – 9%; D5 Sedge and reedbeds, normally without free-standing water – 1%; E1 Dry grasslands – 1%; E3 Seasonally wet and wet grasslands – 0.4%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 8%; G3 Coniferous woodland – 55.4%; G4 Mixed deciduous and coniferous woodland – 22%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 318 Land use: forestry – minor, mowing / hay making – minor, nature conservation and research – 97%. Protected areas: includes Poliskyi nature resrve (20858 ha), includes Didove Ozero state hydrological reserve (294 ha), includes Plotnytsia state landscape reserve (460 ha), overlaps with Emerald Site “Poliskyi” (22966 ha). Threats: abandonment/reduction of land management – low, burning of vegetaion – low, water (drainage) – low. General description. Complex of Pinus sylvestris forests on luvioglacial sands, with 319 oligotrophic, mesotrophic and eutrophic mires. Most constant species of pine forests are Betula pendula, Dicranum polysetum, Pleurozium schreberi. Oten these species are dominants. Dry lichen forests difer by presence and dominance of Calluna vulgaris, Cladonia rangiferina, Cladonia aplestris, Corynephorus canescens, Polytrichum piliferum. Mesic pine forests have high constancies of Calamagrosis epigeios, Calluna vulgaris, Chamaecyisus zingeri, Festuca ovina. Constant diferenial species of wet pine forests are Frangula alnus, Molinia caerulea, Populus tremula, Quercus robur, Sorbus aucuparia, Vaccinium viis-idaea, Vaccinium myrilus. Swamp pine forests difer from wet ones by presence of Andromeda polifolia, Eriophorum vaginatum, Polytrichum alpestre, Sphagnum cuspidatum, Sphagnum fallax, Vaccinium oxycoccos (Oxycoccus palustris), Vaccinium uliginosum. Constant species of raised bogs are Andromeda polifolia, Betula pubescens, Calluna vulgaris, Eriophorum vaginatum, Ledum palustre, Vaccinium oxycoccos, Pinus sylvestris, Polytrichum alpestre, Sphagnum centrale, Sphagnum cuspidatum, Sphagnum fallax, on hummocks – Sphagnum magellanicum. Usually they have an open tree layer of low Pinus sylvestris and Betula pubescens. Most frequent dominants of the lower layers are Eriophorum vaginatum, Sphagnum cuspidatum, Sphagnum fallax. Transiion mires usually are dominated by Carex lasiocarpa, Sphagnum recurvum s.l., Sphagnum cuspidatum. Oten they have a tree layer of Pinus sylvestris and Betula pubescens. Other constant species are Eriophorum vaginatum and Polytrichum alpestre. Eutrophic mires are dominated by Carex elata and Carex rostrata. Botanical significance. Important for conservation of mires and pine forests. Criterion C • C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; area: 0.1 ha; trend: stable; area data quality: poor; trend data quality: poor; note: Juncus bulbosus. • D2.3 Transition mires and quaking bogs; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: poor. • G3.E Nemoral bog conifer woodland; area: 1500 ha; trend: stable; area data quality: poor; trend data quality: poor. • X04 Raised bog complexes; area: 200 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Андрієнко Т.Л. ПЗ Полівський // Фіторізноманіття заповідників і національних природних парків України. Ч.1. Біосферні заповідники. Природні заповідники / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ, 2012. – С. 301–312. 2. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 216 с. 3. Андриенко Т.Л., Попович С.Ю., Шеляг-Сосонко Ю.Р. Полесский государственный заповедник. Растительный мир. – Киев: Наук. думка, 1986. – 208 с. 4. Балашов Л.С., Мошкова Н.О. Синузії деяких водоростей асоціації водяного горіха (Trapa rossica V.Vassil.) в заплаві р. Уборті // Укр. ботан. журн. – 1973. – 3, № 3. – С. 360–364. 5. Бумар Г.Й. Chamaedaphne calyculata (L.) Moench. на Житомирському Полiссi // Укр. ботан. журн. – 1990. – 47, № 4. – С. 73–74. 6. Водно-болотні угіддя України / Під ред. Г.Б. Марушевського, І.С. Жарук. – К.: Wetlands International Black Sea Programme, 2006. – 312 с. 7. Воробйов Є.О., Балашов Л.С., Соломаха В.А. Синтаксономія рослинності Поліського природного заповідника // Укр. фітоцен. зб. – 1997. Сер. Б, вип. 1(8). – К., 1997. – 128 с. 320 8. Маслова В.Р. Лишайники Поліського заповідника // Укр. ботан. журн. – 1977. – 34, № 1. – С. 55–61. 9. Орлов О.О. Рідкісні та зникаючі види судинних рослин Житомирської області. – Житомир: Волинь, 2005. – 496 с. 10. Парахонська Н.О., Мошкова Н.О. Рослинний покрив болота Волисок у Поліському заповіднику та деякі його альгосинузії // Укр. ботан. журн. – 1975. – 32, № 6. – С. 741–746. 11. Партика Л.Я. До бріофлори Поліського природного заповідника. – Укр. ботан. журн. – 1974. – 31, № 6. – С. 770–773. 12. Партика Л.Я. Бриофлора // Полесский государственный заповедник. Растительный мир. – Киев: Наук. думка, 1986. – С. 34–41. 13. Поліському природному заповіднику – 30 років. – Зб. наук. праць. – Вип. 1. – Житомир, 1999. – 144 с. 14. Попович С.Ю. Флористичні знахідки на території Поліського державного заповідника // Укр. ботан. журн. – 1983. – 40, № 6. – С. 94–98. 15. Фіторізноманіття Поліського природного заповідника: водорості, мохоподібні, судинні рослини / за заг. ред. к.б.н. О.О. Орлова. – К.: НВП Інтерсервіс, 2013. – 256 с. 16. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Uholka – Shyrokyi Luh V.A. Onyshchenko Ukrainian name: Уголька – Широкий Луг. Area: 14485.0 ha. Altitude: 370–1501 m. Latitude: 48°17’52” N (48.2979°). Longitude: 23°41’14” E (23.6873°). Administrative regions. Zakarpatska region: Khust raion, Tiachiv raion. Ownership: state (major), private. Biogeographic regions: alpine. Habitats. Level 1. C – 0.2%; E – 4.0%; G – 95.7%; H – 0.1%. Habitats. Level 2. C2 Surface running waters – 0.2%; E1 Dry grasslands – 1.9%; E2 Mesic grasslands – 0.3%; E4 Alpine and subalpine grasslands stands – 1.8%; G1 Broadleaved deciduous woodland – 95.6%; G3 Coniferous woodland – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.1%. Futher habitat description. C2.1 Springs, spring brooks and geysers; C2.2 Permanent nontidal, fast, turbulent watercourses; E1.7 Non-Mediterranean dry acid and neutral closed grassland (E1.71 Nardus stricta swards, E1.72 Agrosis – Festuca grassland); E2.2 Low and medium alitude hay meadows; G1.6 Fagus woodland; G3.F Highly artificial coniferous plantations; H2.3 Temperate-montane acid siliceous screes; H2.4 Temperate-montane calcareous and ultra-basic screes; H3.1 Acid silicious inland clifs; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – minor, forestry – minor, mowing/hay making – minor, nature conservation and research – major. 321 Protected areas: included in Karpatskyi biosphere reserve (naional category), included in Carpathian biosphere reserve (UNESCO), included in World Heritage Site “Primeval Beech Forests of the Carpathians and the Ancient Beech Forests of Germany” (14485 ha; core zone: 11860 ha, bufer zone: 2625 ha), included in Emerald Site “Carpathian Biosphere Reserve”. Threats: –. • Neckera pennata Hedw.; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. Criterion B • G1 deciduous broadleaved woodland; area 13860 ha; % of indicator species: 20.8%; No of indicator species: 16; trend: increasing; species data quality: good; area data quality: good; trend data quality: good. Criterion C • G1.6 Fagus woodland (excluding G1.66); area: 13800 ha; trend: stable; area data quality: good; trend data quality: good. • G1.66 Medio-European limestone Fagus forests (*9150); area: 10 ha; trend: stable; area data quality: medium; trend data quality: good. Literature 1. Brändli U.-B., Dovhanych Y. Virgin forest of Uholka: Nature Guide to the Largest Virgin Beech Forest of Europe. A UNESCO World Heritage Site. WSL, Rakhiv: Birmensdorf and CBR, 2008 – 23 p. 2. Гамор Ф.Д., Волощук М.І., Антосяк Т.М., Козурак А.В. БЗ Карпатський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 45–72. 3. Гамор Ф.Д., Довганич Я.О., Покиньчереда В.Ф. та ін. Праліси Закарпаття. Інвентаризація та менеджмент. – Рахів, 2008. – 86 с. 4. Біорізноманіття Карпатського біосферного заповідника / Кол. авт., Ред. рада: Я.І. Мовчан, Ф.Д. Гамор та ін. – К.: Інтерекоцентр, 1997. – 711 с. 5. Онищенко В.А. Лісова рослинність верхньої частини басейну Малої Угольки (Карпатський біосферний заповідник) // Науковий вісник Чернівецького університету. – 2007. – Вип. 343: Біологія. – С. 130–147. 6. Праліси в центрі Європи: Путівник по лісах Карпатського біосферного заповідника / Кол. авт., ред.: У-Б. Брендлі, Я. Довганич. – Бірменсдорф: Швейцарський федеральний ін-т досліджень лісу, снігу і ландшафтів (WSL) – Рахів: Карпатський біосферний заповідник (КБЗ), 2003. – 192 с. 7. Флора і рослинність Карпатського заповідника / Стойко С.М., Тасенкевич Л.О., Мілкіна Л.І. та ін. – К.: Наук. думка, 1982. – 220 с. Usia – Shutnivtsi General description. The beech forest occupies about 95% of the area. Predominantly it is the neutrophilous forest. The tree layer usually consists of Fagus sylvaica. Constant species are Acer pseudoplatanus, Athyrium ilix-femona, Dentaria bulbifera (Cardamine bulbifera), Dentaria glandulosa (Cardamine glandulosa), Dryopteris ilix-mas, Galium odoratum, Rubus hirtus. Acidophilous beech forests occupies a smaller area. Besides there are calcareous beech forests. They difer by presence of Tilia platyphyllos, Taxus baccata, Carex digitata, Hepaica nobilis, Meliis carpaicum, Moehringia muscosa, Primula acaulis, Seseli libanois. Botanical significance. Probably this is the largest primeval beech forest in Europe. Criterion A • Mannia triandra (Scop.) Grolle; A(ii); abundance: rare; trend: unknown; species data quality: poor; trend data quality: poor. 322 L.H. Lubinska, V.A. Kolodiy Ukrainian name: Устя – Шутнівці. Area: 46.5 ha. Altitude: 122–210 m. Latitude: 48°35’07” N (48.5853°). Longitude: 26°37’32” E (26.6255°). Administrative regions. Kmelnytskyi region: Kamianets-Podilskyi raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 9.6%; F – 7.4%; G – 70.0%; H – 13.0%. Habitats. Level 2. E1 Dry grasslands – 9.6%; F3 Temperate and mediterranean-montane 323 scrub – 7.4%; G1 Broadleaved deciduous woodland – 70.0%; H2 Screes – 1.0%; H3 Inland clifs, rock pavements and outcrops – 12.0%. Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Vasylivka V.P. Kolomiychuk, L.V. Markivska Ukrainian name: Василівка. Area: 132.5 ha. Altitude: 153–235 m. Latitude: 48°14’37” N (48.2436°). Longitude: 29°18’41” E (29.3114°). Administrative regions. Vinnytsia region: Chechelnyk raion. Ownership: state. Biogeographic regions: coninental Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs. Land use: agriculture (animals) – minor, forestry – minor, nature conservation and research – major, tourism/recreaion – minor. Protected areas: included in Podilski Tovtry naional nature park (zone of regulated recreaion), included in Emerald Site “Podilski Tovtry Naional Nature Park”. Threats: agricultural intensification/expansion (grazing) – low, development (recreaion/ tourism) – low. General description. Steep slopes of the Smotrych river valley with calcareous rocks, shrub vegetaion dominated by Prunus spinosa, and deciduous forest. Typical species of the outcrops are Aurinia saxatilis, Sedum acre, Allium podolicum, Potenilla arenaria, Sipa capillata, Veronica incana, Festuca valesiaca, Sesleria heuleriana, Teucrium chamaedrys, T. pannonicum, Thymus moldavicus, Scabiosa ochroleuca, Schivereckia podolica (Draba podolica), Anthericum ramosum. The area belongs to the zone of regulated recreaion of naional nature park “Podiliski Tovtry”. Botanical significance. One of the best populaions of Schivereckia podolica in Ukraine. Criterion A • Schivereckia podolica (Besser) Andrz. et Besser ex DC. (Draba podolica (Besser) Rupr.); A(ii); abundance: frequent; trend: unknown; species data quality: good; trend data quality: poor. Habitats. Level 1. E – 95.0%; F – 1.0%; G – 3.0%; H – 1.0% Habitats. Level 2. E1 Dry grasslands – 94.7%; E7 Sparsely wooded grasslands – 0.3%; G1 Broadleaved deciduous woodland – 1.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes. Land use: nature conservaion and research – minor. Protected areas: includes regional botanical reserve “Romashkove” 8.7 ha (a part of Karmeliukove Podillia naional nature park), overlaps with Emerald Site “Karmeliukove 324 325 Podillia Naional Nature Park” 8.7 ha). Threats: abandonment/reducion of land management – low, agricultural intensiicaion/ expansion (grazing) – low, burning of vegetaion – low. General description. Slopes with the steppe vegetaion dominated by Festuca valesiaca, Elytrigia intermedia, Poa angusifolia, Sipa capillata, with presence of Botryochloa ischaemum, Bromopsis inermis, Chamaecyisus austriacus, Convolvolus arvensis, Elytrigia repens, Euphorbia cyparissias, Galium verum, Inula encifolia, Koeleria cristata, Salvia pratensis, Salvia vericillata, Securigera varia, Stachus recta, Teucrium chamaedrys. Botanical significance. Important area for Carlina onopordifolia. Criterion A • Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł.; A(i), A(ii), A(iv); abundance: occasional (1400 individuals); trend: stable; species data quality: good; trend data quality: poor. Conservaional proposals. Include enire IPA in naional nature park “Karmeliukove Podillia”. Literature 1. Kuzemko A.A., Becker T., Didukh Y.P., Ardelean I.A., Becker U., Beldean M., Dolnik C., Jeschke M., Naqinezhad A., Ugurlu E., Ünal A., Vassilev K., Vorona E.I., Yavorska O.H., Dengler J. Dry grassland vegetation of Central Podolia (Ukraine) – a preliminary overview on syntaxonomy, ecology and biodiversity // Tuexenia. – 2014. – Vol. 34. – S. 391–430. 2. Дідух Я.П., Кагало О.О., Орлов О.О. Відкасник татарниколистий Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł. / Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – C. 279. 3. Мельник В.І., Скоропляс І. О., Ваколюк В. Д. Carlina onopordifolia (Asteraceae) на Східному Поділлі // Укр. ботан. журн. – 2014. – 71, №3. – С. 324–329. 4. Польовий Є.В., Дідух Я. П. Еколого-територіальна диференціація рослинного покриву модельного полігону “Ромашково” в долині р. Савранки (Вінницька обл.) // Укр. ботан. журн. – 2014. – 71, №6. – С. 647–659. 5. Яворська О.Г. НПП Кармелюкове Поділля // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ, 2012. – С. 265–272. sparse or no vegetation – 0.8%. Futher habitat description. C2.5 Temporary running waters; E1.2 Perennial calcareous grassland and basic steppes; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Василівський і Розкопинський яри. Transliteraion/Translaion variants: Vasylivs’kyi and Rozkopyns’kyi Ravines. Area: 1962 ha. Altitude: 84–263 m. Latitude: 48°30’08” N (48.5021°). Longitude: 27°25’36” E (27.4263°). Administrative regions. Chernivtsi region: Sokyriany raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 0.2%; G – 99.0%; H – 0.8%. Habitats. Level 2. C2 Surface running waters – 0.0%; E1 Dry grasslands – 0.2%; G1 – Broadleaved deciduous woodland – 99.0%; H5 Miscellaneous inland habitats with very Land use: forestry – major, nature conservation and research – minor. Protected areas: includes (about 497 ha) with regional landscape reserve “Vasilivskyi Yar”. Threats: forestry (intensiied forest management) – medium. General description. Broadleaved forests dominated by Quercus robur, Carpinus betulus, Acer pseudoplatanus, Fraxinus excelsior with admixture of Acer campestre, Acer platanoides, Tilia cordata, Sorbus torminalis. The shrub layer is composed of Acer tataricum, Acer campestre, Corylus avellana, Euonymus verrucosus, Euonymus europaeus, Sambucus nigra, Staphylea pinnata, Swida sanguinea (Cornus sanguinea), Viburnum lantana. Typical species of the herb layer are Carex pilosa, Stellaria holostea, Asarum europaeum, Aegopodium podagraria, Convallaria majalis, Galium odoratum, Lathyrus vernus, Hedera helix, Hepatica nobilis. There scatered limestone boulders up to 3 m in diameter, covered by mosses and Phylliis scolopendrium. Botanical significance. Important area for Friillaria montana and Aconitum besserianum. Criterion А • Fritillaria montana Hoppe; А (ii); abundance: occasional (5000 individuals); trend: stable; species data quality: good; trend data quality: poor. • Aconitum besserianum Andrz. ex Trautv; А (iiі); abundance: rare; trend: stable; species data quality: medium; trend data quality: poor. 326 327 Vasylivskyi i Rozkopynskyi Yary Literature 1. Волуца О.Д. Fritillaria montana Hoppe у флорі Чернівецької області // Науковий вісник Чернівецького університету: Збірник наукових праць. – Вип. 293: Біологія. – Чернівці: Рута, 2006. – С. 31–34. 2. Волуца О. Euonymus nana M. Bieb. (Celastraceae) – новий вид для флори ПрутДністровського межиріччя (в межах України) // Вісник Прикарпатського національного університету імені Василя Стефаника. Серія Біологія / Матеріали Міжнародної наукової конференції “Проблеми вивчення та охорони біорізноманіття Карпат та прилеглих територій” (Івано-Франківськ, 8-9 листопада 2007р.). – Вип. VII-VIII. – Івано-Франківськ: Гостинець, 2007. – С. 51-52. 3. Волуца О.Д. Нові місцезнаходження видів роду Pulsailla Mill. (Ranunculaceae) на території Північно-Бессарабського геоботанічного округу (Чернівецька область) // “Молодь у вирішенні регіональних та транскордонних проблем екологічної безпеки”: Матеріали Шостої Міжнародної наукової конференції (м. Чернівці, 11–12 травня 2007 року). – Чернівці: Зелена Буковина, 2007. – С. 59–61. 4. Волуца О.Д., Токарюк А.І. Стан популяції Friillaria montana Hoppe (Liliaceae) в околицях м. Сокиряни (Чернівецька область) // “Молодь та поступ біології”: Збірник тез IV Міжнародної конференції студентів і аспірантів (7-10 квітня 2008 року, м. Львів). – Львів, 2008. – С. 119-120. 5. Каземірська М.А., Чорней І.І. Fritillaria montana Hoppe (Liliaceae): географічна характеристика, поширення в Україні // Науковий вісник Чернівецького університету. Біологія (Біологічні системи). – 2010. – Т. 2, Вип. 3. – С. 63–68. 6. Каземірська М.А., Чорней І.І. Вікова та просторова структури популяцій Fritillaria montana Hoppe у Прут-Дністровському межиріччі // Біологічні системи. – 2010. – Т. 2., Вип. 2. – С. 62–66. 7. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 8. Чорней І.І., Буджак В.В., Токарюк А.І. Сторінками Червоної книги України (рослинний світ). Чернівецька область. – Чернівці: ДрукАрт, 2010. – C. 85–87. trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 1.5%; H3 Inland cliffs, rock pavements and outcrops – 0.1%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; E7.2 Sub-coninental parkland; F3.1 Temperate thickets and scrub; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G3.F Highly artificial coniferous plantations; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H3.2 Basic and ultra-basic inland cliffs; H3.5 Almost bare rock pavements, including limestone pavements. Land use: agriculture (animals) – minor, nature conservation and research – minor, forestry Velyki Holdy N.V. Shumska, V.A. Onyshchenko Ukrainian name: Великі Голди. Area: 141 ha. Altitude: 260–347 m. Latitude: 49°19’32” N (49.3255°). Longitude: 24°39’54” E (24.6650°). Administrative regions. Ivano-Frankivsk region: Rohatyn raion. Ownership: state. Biogeographic regions: coninental Habitats. Level 1. E – 21.9%; F – 2.0%; G – 76.0%; H – 0.1% Habitats. Level 2. E1 Dry grasslands – 21.5%; E5 Woodland fringes and clearings and tall forb stands – 0.1%; E7 Sparsely wooded grasslands – 0.3%; F3 Temperate and mediterraneanmontane scrub – 2.0%; G1 Broadleaved deciduous woodland – 55.0%; G3 Coniferous woodland – 19.0%; G4 Mixed deciduous and coniferous woodland – 0.5%; G5 Lines of 328 – major, mowing/hay making – minor. Protected areas: includes state complex nature monument “Velyki Holdy” (24.0 ha), included in Emerald Site “Velyki Holdy”. Threats: abandonment/reducion of land management – medium, agricultural intensiicaion/expansion (grazing) – low, burning of vegetaion – low. General description. Hills with the deciduous forest, pine plantaions, dry grasslands, shrubs, and gypsum outcrops. The grasslands are dominated by Brachypodium pinnatum, Briza media, Elytrigia intermedia. Other typical species are Anthericum ramosum, Bupleurum falcatum, Carex montana, Dactylis glomerata, Salvia pratensis. In upper parts of the slopes and on eroded stony slopes, dominant species are Sipa capillata, Sipa pennata, Festuca valesiaca, Carex humilis, Koeleria cristata, Teucrium chamaedrys, Astragalus onobrychis, other frequent species are Artemisia austriaca, Euphorbia cyparissias, Inula ensifolia, Phleum phleoides, Thymus marschallianus. On gypsum outcrops, there prevail Allium lusitanicum s.l. (Allium montanum auct.), Festuca pallens, Gypsophila fasigiata, Potenilla 329 arenaria, Sedum acre. Main dominant of the shrub vegetaion is Prunus spinosa. The area of trees and shrubs is increasing, this is the main threat for conservaion of Carlina cirsioides and other species of grasslands. Botanical significance. Important area for Carlina onopordifolia. Criterion A • Carlina onopordifolia Besser ex Szafer, Kulcz. et Pawł.; A(i), A(ii), A(iv); abundance: frequent (2000 individuals); trend: stable; species data quality: good; trend data quality: medium. Conservaional proposals: do not allow natural and ariicial aforestaion, expand area of nature monument “Velyki Holdy”. Literature 1. Шумська Н.В., Чуй О.В., Дмитраш І.І. Збереження фіторізноманіття комплексної пам’ятки природи “Великі Голди” (Рогатинське Опілля) шляхом оптимізації її території // Науковий вісник національного університету біоресурсів і природокористування України. Сер.: Лісівництво та декоративно садівництво. – 2012. – 171 (1). – С. 287–290. Verbetska Tovtra Ukrainian name: Вербецька товтра. Area: 10.8 ha. Altitude: 280–303 m. Latitude: 48°48’33” N (48.8092°). Longitude: 26°36’14” E (26.6038°). Administrative regions. Kmelnytskyi region: Kamianets-Podilskyi raion. Ownership: state Biogeographic regions: coninental. V.A. Onyshchenko scrub – 1.1%; H2 Screes – 0.1%; H3 Inland clifs, rock pavements and outcrops – 1.2%. Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs. Land use: nature conservation and research – major. Protected areas: overlaps (about 8 ha) with Tovtra Verbetska state botanical reserve, included in Podilski Tovtry naional nature park, included in Emerald Site “Podilski Tovtry Naional Nature Park”. Threats: agricultural intensification/expansion (arable) – low, development (recreaion/ tourism) – low. General description. A small hill with the steppe vegetaion and limestone outcrops. Steppe vegetaion is dominated by Carex humilis, Festuca valesiaca, Sipa capillata, Sesleria heuleriana. On the outcrops, there are Allium lavescens, Allium lusitanicum, Allium podolicum, Sedum acre, Sempervivum ruthenicum, Veronica incana. Botanical significance. Important area for Gypsophila thyraica. Criterion A • Gypsophila thyraica Krasnova; A(iii); abundance: frequent; trend: unknown; species data quality: poor; trend data quality: poor. Literature 1. Заповідні перлини Хмельниччини / під ред. Т.Л.Андрієнко. – Хмельницький: ПАВФ “Інтрада”, 2006. – 220 с. Verkhniobuzki Lisy Habitats. Level 1. E – 97.6%; F – 1.1%; H – 1.3%. Habitats. Level 2. E1 Dry grasslands – 97.6%; F3 Temperate and mediterranean-montane V.A. Onyshchenko Ukrainian name: Верхньобузькі ліси. Transliteraion/Translaion variants: Upper Buh Forests. Area: 6543.5 ha. Altitude: 270–437 m. Latitude: 49°52’56” N (49.8823°). Longitude: 25°01’30” E (25.0249°). Administrative regions. Lviv region: Brody raion; Zolochiv raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 2.1%; G – 96.9%; H – 1.0%. Habitats. Level 2. E2 Mesic grasslands – 1.6%; E3 Seasonally wet and wet grasslands – 0.5%; G1 Broadleaved deciduous woodland – 94.5%; G3 Coniferous woodland – 0.4%; G4 Mixed deciduous and coniferous woodland – 2.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion. E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.2 Mixed riparian floodplain and gallery woodland; G1.6 Fagus woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G3.F Highly artificial coniferous forestry plantations; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; H5.6 Trampled areas. Land use: forestry – major, nature conservation and research – 83%. 330 331 Protected areas: overlaps with Pivnichne Podillia naional nature park (5920 ha), includes Pamiatka Peniatska regional complex nature monument (35 ha), overlaps (65 ha) with Pidlyska Hora regional complex nature monument, includes Sasivska regional botanical nature monument (130 ha), includes Sviata Hora regional complex nature monument (186 ha), includes regional complex nature monument “Zhulytska Hora, Hora Storozhykha, Hora Vysoka” (261 ha), overlaps with Emerald Site “Pivnichne Podillia” (about 5920 ha). Ranunculus lanuginosus. Besides there are mixed Quercus robur – Pinus sylvestris forests and Alnus gluinosa forests. Botanical significance. Important area for conservaion of species-rich broadleaved forests. Criterion B • G1 Broadleaved deciduous woodland; area: 5800 ha; % of indicator species: 13.0%; No of indicator species: 10; trend: increasing; species data quality: good; area data quality: good; trend data quality: medium. Criterion C • G1.66 Medio-European limestone Fagus forests (*9150); area: 500 ha; trend: stable; area data quality: poor; trend data quality: good. • G1.A4 (*9180) Ravine and slope woodland; area: 200 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Кагало О.О. Північне Поділля // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 381–394. 2. Рало В. М. Матеріали до класифікації букових лісів Верхобузького пасма (північно-західне Поділля) // Наукові основи збереження біотичної різноманітності / Тематичний збірник Інституту екології Карпат НАН України. – Вип. 8–9. – Львів, 2009. – С. 65–102. 3. Рало В.М., Онищенко В.А. Anthrisco nitidi-Aceretum pseudoplatani – нова асоціація із Західного Поділля // Науковий вісник Волинського національного університету імені Лесі Українки. Біологічні науки. – 2008. – № 3. – С. 239–249. Vitrohon V.A. Onyshchenko Ukrainian name: Вітрогон. Area: 688.0 ha. Altitude: 70–140 m. Threats: forestry (intensiied forest management) – low. General description. Hills covered by broadleaved forests. The largest area is occupied by Fagus sylvaica forests. Main dominants of the herb layer are Aegopodium podagraria, Anemone nemorosa, Asarum europaeum, Carex pilosa, Galium odoratum, Hedera helix, Lamium galeobdolon. Constatnt species are Acer platanoides, Acer pseudoplatanus, Anemone nemorosa, Carex digitata, Dryopteris ilix-mas, Fagus sylvaica, Galium odoratum, Lamium galeobdolon, Maianthemum bifolium, Polygonatum mulilorum. Calcareous beech forests difer by constant presence of Cephalanthera damasonium, Campanula persicifolia, Campanula trachelium, Convallaria majalis, Daphne mezereum, Lilium martagon, Meliis sarmaica (M. melissophyllum s.l.), Neoia nidus-avis, Swida sanguinea (Cornus sanguinea), Viola mirabilis. Species comoposiion of oak-hornbeam forests (Quercus robur, Carpinus betulus) is similar to one of beech forests. On slopes and botoms of valleys and gullies, there are species-rich forests with Fraxinus excelsior and Acer pseudoplatanus prevailing in the tree layer. Their characterisic species are Anthrisus niida, Campanula laifolia, Cerasium sylvaicum, Chaerophyllum aromaicum, Dipsacus pilosus, Primula elaior, 332 Latitude: 49°07’59” N (49.1331°). Longitude: 39°42’25” E (39.7068°). 333 Administrative regions. Luhansk region: Bilovodsk raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 0.2%; E – 96.6%; F – 2.0%; G – 0.6%; H – 0.5%; J – 0.1%. Habitats. Level 2. C1 Surface standing waters – 0.1%; C2 Surface running waters – 0.1%; E1 Dry grasslands – 93.0%; E2 Mesic grasslands – 3.6%; F3 Temperate and mediterraneanmontane scrub – 2.0%; G1 Broadleaved deciduous woodland – 0.6%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%; J4 Transport networks and other constructed hard-surfaced areas – 0.1%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.2 Submediterranean deciduous thickets and brushes; H5.6 Trampled areas. Land use: agriculture (animals) – minor. Protected areas: overlaps (350–400 ha) with proposed regional botanical reserve “Vitrohon”, overlaps (647 ha) with Emerald Site “Vitrohonskyi”. Threats: agricultural intensification/expansion (arable) – low, agricultural intensiicaion/ expansion (grazing) – low, forestry (aforestaion) – low. General description. Small valleys with the steppe vegetaion (abandoned pastures) on the slopes. Major dominants are Festuca valesiaca s.l., Sipa capillata, Sipa irsa, Sipa ucrainica, Sipa zalesskii. Botanical significance. Important area for conservaion of the steppe vegetaion and some steppe species. Criterion A • Paeonia tenuifolia L.; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. • Stipa zalesskii Wilensky; A(ii); abundance: frequent; trend: stable; species data quality: medium; trend data quality: medium. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 600 ha; trend: stable; area data quality: good; trend data quality: medium. Conservaion proposals. Сreate an Emerald Site including the enire IPA. Volyzhyn Lis V.A. Onyshchenko, O.Yu. Umanets Ukrainian name: Волижин ліс. Transliteraion/Translaion variants: Volyzhyn Wood. Area: 203.0 ha. Altitude: 0–6 m. Latitude: 46°32’21” N (46.5391°). Longitude: 31°43’14” E (31.7205°). Administrative regions. Mykolaiv region: Ochakiv raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 10.3%; D – 2.6%; E – 74.4%; F – 0.4%; G – 11.8%; H – 0.5%. Habitats. Level 2. Surface standing waters – 8.4%; C3 Littoral zone of inland surface 334 waterbodies – 1.9%; D5 Sedge and reedbeds normally without free-standing water – 2.6%; E1 Dry grasslands – 52.8%; E2 Mesic grasslands – 21.5%; E6 Inland salt steppes – 0.1%; F3 Temperate and mediterranean-mountane scrub – 0.4%; G1 Broadleaved deciduous woodland – 11.8%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.2 Perennial calcareous grassland and basic steppes; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland (× E1.1); E2.5 Meadows of the steppe zone; E6.2 Coninental inland salt steppes; F3.1 Temperate thickets and scrub; G1.5 Broadleaved swamp woodland on acid peat; G1.7 Thermophilous deciduous woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; H5.3 Sparsely- or un-vegetated habitats on mineral substrates not resulting from recent ice activity. Land use: mowing/hay making – minor, nature conservation and research – 67%. Protected areas: included in Chernomorskiy (Chornomorskyi, Black Sea) biosphere reserve (core zone of the reserve), included in Emerald Site “Black Sea Biosphere Reserve”. Threats: –. General description. Major habitat type is the sand steppe. Other important habitats types are freshwater permanent lakes, mesic grasslands, eutrophic mires, deciduous forests (swamp and mesic), halophytic vegetation. Sand steppes are dominated by Artemisia marschalliana, Festuca beckeri, Helichrysum corymbiforme, Koeleria sabuletorum, Thymus borysthenicus, Stipa borysthenica. Typical species: Agropyron dasyanthum, Goniolimon graminifolium, Polygonum arenarium. Prevailing species of mesic grasslands are Agrostis sabulicola, Calamagrosts epigeios, Cynodon dactylon, Elytrigia elongata, Elytrigia repens, Phleum phleoides, Poa angustifolia. Besides there are communiies of Puccinellia gigantea, Salicornia perennans, Tripolium vulgare, Carex riparia, Phragmites australis, Lemna minor, Lemna trisulca. Dominants of the the herb layer of Alder gluinosa swamp woods are Calamagrosis epigeios, Carex riparia. Constant species: Eupatorium cannabinum, Lysimachia vulgaris, Urica dioica. In Betula borysthenica woods, the shrub layer consists of Rhamnus catharica, Sambucus nigra. Dominants of the herb layer are Agrostis sabulicola, Calamagrostis epigeios, Carex elata, Phragmites australis. Botanical significance. Important area for conservaion of steppe swamp Alnus gluinosa 335 woods and some psammophyic species. Criterion A • Allium savranicum Besser; A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Alyssum savranicum Andrz. ex Besser (Odontarrhena savranica (Andrz. ex Besser) D.A.German); A(iv); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. • Goniolimon graminifolium (Ait.) Boiss.; A(iv); abundance: frequent; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • G1.414 Steppe swamp Alnus gluinosa woods; area: 11 ha; trend: stable; area data quality: good; trend data quality: medium. Literature 1. Кузнєцова Г.О., Протопопова В.В., Саричева З.А. Флора і рослинність Волижиного лісу в Чорноморському заповіднику // Укр. ботан. журн. – 1969. – 26. № 4. – С. 35–40. 2. Уманець О.Ю. БЗ Чорноморський // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 73–93. Threats: abandonment/reducion of land management – low; burning of vegetaion – medium, extracion (minerals/quarries) – low, forestry (aforestaion) – medium. General description. Slopes of the valley of the Vovcha river with chalk outcrops. The major habitat type is the steppe. Dominants of the steppe vegetaion are Bromopsis riparia, Carex humilis, Caragana frutex, Chamaecyisus austriacus, Chamaecythisus ruthenicus, Festuca valesiaca, Koeleria cristata, Poa angusifolia, Sipa capillata, Sipa pulcherrima, Sipa pennata, Salvia nutans. Major dominants of the chalk outcrops are Thymus cretaceus, Artemisia hololeuca, Asperula tephrocarpa, Onosma tanaiica. Someimes there dominate Androsace koso-poljanskii, Hyssopus cretaceus, Linum ucrainicum, Onosma tanaiica, Polygala cretacea, Scutellaria creicola, Ephedra distachia. Other species of the outcrops: Gypsophila alissima, Helianthemum cretaceum. Natural forests are dominated by Quercus robur, Tilia cordata, Acer platanoides. There are also plantaions of Pinus sylvestris, Pinus pallasiana, Quercus robur, Fraxinus excelsior, Tilia cordata, Cotynus coggygria. Rare endemic species Vovchanski Skhyly V.A. Onyshchenko, O.V. Bezrodnova, M.V. Banik Ukrainian name: Вовчанські схили. Transliteraion/Translaion variants: Vovcha Slopes. Area: 1131.6 ha. Altitude: 120–200 m. Latitude: 50°22’35” N (50.3763°). Longitude: 37°17’23” E (37.2898°). Administrative regions. Kharkiv region: Vovchansk raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 72.7%; F – 2.0%; G – 17.3%; H – 8.0%. Habitats. Level 2. E1 Dry grasslands – 72.7%; F3 Temperate and mediterranean-montane scrub – 2.0%; G1 Broadleaved deciduous woodland – 15.4%; G3 Coniferous woodland – 1.9%; H2 Screes – 8.0%. Futher habitat description. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; G1.C Highly artificial broadleaved deciduous forestry plantations; G3.F Highly artificial coniferous plantations; H2.6 Calcareous and ultra-basic screes of warm exposures. Land use: agriculture (animals) – major; forestry – minor, nature conservaion and research – minor. Protected areas: includes Vovchanskyi state botanical reserve (185 ha), overlaps (18 ha) with Siverskodonetskyi regional landscape reserve, overlaps (about 1050 ha) with Emerald Site “Siverskodonetskyi”. 336 Daphne sophia occurs mainly at forest margins. Botanical significance. Important area for conservaion of endemic species Daphne sophia and Androsace koso-poljanskii and vegetaion of chalk outcrops. Criterion A • Androsace koso-poljanskii Ovcz.; A(iv); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. • Daphne sophia Kalen.; A(i), A(iv); abundance: rare (675 individuals in 3 localiies); trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.13 Coninental dry rocky steppic grasslands and dwarf scrub on chalk outcrops; area: 90 ha; trend: stable; area data quality: medium; trend data quality: medium. 337 Literature 1. Banik M. Daphne’04. Final report. – Kharkiv, 2006. – 20 p. (http://www.rufford.org/ files/.01.04%20Detailed%Final%20Report.pdf). 2. Банік М.В., Тверетинова В.В., Волкова Р.Є., Атемасова Т.А., Атемасов А.А., Брезгунова О.О., Влащенко А.С., Гончаров Г.Л., Коноваленко С.В., Скоробогатов В.М., Скоробогатов Є.В., Целіщев О.Г. Нові місцезнаходження Daphne sophiae Kalen., (Thymeleaceae) в Україні // Укр. ботан. журн. – 2007. – 64, № 4. – С. 565–569. 3. Ермоленко Е.Д., Горелова Е.Н., Кушнарева Ю.И. К флоре и растительности меловых обнажений рек Волчьей и Оскол в Харьковской области // Вест. ХГУ. – 1981. – № 211. – С. 6–11. 4. Коротченко І.А. Рідкісні види флори степів південної частини Лівобережного Лісостепу України // Наукові основи збереження біотичної різноманітності / Темат. зб. ін-ту екології Карпат НАН України. – Вип. 3. – Львів: Ліга-Прес, 2001. – С. 26–36 5. Расевич В.В. Еколого-ценотичні особливості популяцій Daphne sophia Kalen. у природній флорі України // Укр. ботан. журн. – 2008. – 65, № 1. – С. 90–103. 6. Смолко С.С. Третинний релікт – вовчі ягоди Софії (Daphne sophia Kalen.) на Середньоросійській височині та його сучасне поширення // Укр. ботан. журн. – 1967. – 24, № 1. – С. 69–75. 7. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Vtenske Boloto V.A. Onyshchenko Ukrainian name: Втенське болото. Transliteraion/Translaion variants: Vtenske Swamp, Vtenske Bog. Area: 179 ha. Altitude: 155–160 m. Latitude: 51°37’31” N (51.6251°). Longitude: 23°41’01” E (23.6835°). Administrative regions. Volynska region: Shatsk raion. Ownership: state. Biogeographic regions: continental. Habitats. Level 1. G – 100%. Habitats. Level 2. G1 Broadleaved deciduous woodland – 4.0%; G3 Coniferous woodland – 76.0%; G4 Mixed deciduous and coniferous woodland – 20.0%. Futher habitat description. G1.5 Broadleaved swamp woodland on acid peat; G3.E Nemoral bog conifer woodland, G4.1 Mixed swamp woodland. Land use: nature conservation and research – 100%. Protected areas: includes Vtenskyi state botanical reserve (130 ha), included in biosphere reserve “West Polesie”, included in Shatskyi naional nature park, included in Emerald Site “Shatskyi”. Threats: water (drainage) – low. General description. Wooded bog. The tree layer is dominated by low Pinus sylvestris, oten with admixture of Betula pubescens. Dominant species of the lower layers are Sphagnum magellanicum, Sphagnum angusifolium, Eriophorum vaginatum, Vaccinium oxycoccos 338 (Oxycoccus palustris). Other frequent species: Ledum palustre, Andromeda polifolia, Drosera rotundifolia, Calluna vulgaris. Botanical significance. Important site of Pinus sylvestris bogs. Criterion C • G3.E Nemoral bog conifer woodland; area: 90 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Природно-заповідний фонд Волинської області / Упор.: М. Химин та ін. – Луцьк: Ініціал, 1999. – 48 с. 2. Фіторізноманіття Українського Полісся та його охорона / Під заг. ред. Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2006. – 316 с. Vymushiv I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Вимушів. Area: 8.8 ha. Altitude: 258–282 m. Latitude: 48°38’31” N (48.6418°). Longitude: 25°39’37” E (25.6602°). Administrative regions. Chernivtsi region: Zastavna raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1: E – 90.0%, F – 9.0%, H – 1.0%. Habitats. Level 2: E1 Dry grasslands – 90.0%; F3 Temperate and mediterranean-montane 339 scrub – 9.0%; H3 Inland cliffs, rock pavements and outcrops – 1.0%. Futher habitat description: E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; H3.2 Basic and ultra-basic inland cliffs. Land use: agriculture (animals) – minor. Vyshnivka I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak Ukrainian name: Вишнівка. Area: 309 ha. Altitude: 244–329 m. Latitude: 48°34’31” N (48.5751°). Longitude: 25°23’53” E (25.3981°). Administrative regions. Ivano-Frankivsk region: Horodenka raion, Sniatyn raion. Ownership: state, private. Biogeographic regions: coninental. Protected areas: –. Threats: abandonment/reducion of land management – low, extracion (mineral/quarries) – low. General description. Steep slopes with dry grasslands and outcrops of gypsum and limestone. Grasslands are dominated by Lembotropis nigricans, Elytrigia intermedia. Frequent species: Adonis vernalis, Agrimonia eupatoria, Anthericum ramosum, Arrhenatherum elatius, Asyneuma canescens, Campanula glomerata, Centaurea jacea, Clematis integrifolia, Crinitaria linosyris, Cruciata glabra, Dactylis glomerata, Eryngium campestre, Falcaria vulgaris, Filipendula vulgaris, Galium verum, Inula ensifolia, Knautia arvensis, Medicago romanica, Salvia pratensis, Salvia verticillata, Scabiosa ochroleuca, Securigera varia, Thalictrum simplex, Trifolium montanum. Botanical significance. Important area for the endemic species Aconitum pseudanthora. Criterion A • Aconitum pseudanthora Błocki ex Pacz. A(iii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Conservaion proposals. Create a state botanical reserve or nature monument. Habitats. Level 1: C – 1.7%, E – 97.3%, F – 1.0%. Habitats. Level 2: C1 Surface standing waters – 1.3%, C3 Littoral zone of inland surface waterbodies – 0.4%, E1 Dry grasslands – 75.3%; E2 Mesic grasslands – 19.0%, E3 Seasonally wet and wet grasslands – 3.0%; F3 Temperate and mediterranean-montane scrub – 1.0%. Futher habitat description: E1.2 Perennial calcareous grassland and basic steppes; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; F3.1 Temperate thickets and scrub. 340 341 Land use: agriculture (animals) – minor. Protected areas: –. Threats: agricultural intensification/expansion (arable) – medium. General description. Grasslands dominated by Brachypodium pinnatum with presence of Arrhenatherum elatius, Briza media, Cirsium pannonicum, Festuca rupicola, Filipendula vulgaris, Galium boreale, Galium verum, Inula salicina, Iris hungarica, Koeleria cristata, Lathyrus pannonicus, Potentilla alba, Prunella grandiflora, Pyrethrum corymbosum, Salvia pratensis, Salvia verticillata, Sanguisorba officinalis, Serratula lycopifolia, Trifolium montanum. Botanical significance. One of the largest areas of dry grasslans in western Ukraine with presence of Pulsailla grandis, Iris hungarica, Serratula lycopifolia. Criterion A • Serratula lycopifolia (Vill.) A. Kern.; А (ii); abundance: rare; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 70 ha; trend: stable; area data quality: good; trend data quality: medium. Conservaion proposals. Do not allow land plowing. Create a state botanical reserve and an Emerald Site. austriacum, Dryopteris dilatata, Dryopteris carthusiana, Geniana asclepiadea, Luzula pilosa, Luzula sylvaica, Polytrichum formosum, Prenanthes purpurea, Sorbus aucuparia, Vaccinium viis-idaea. Pinus cembra is the main dominant in an area of 18 ha. Besides there are Pinus mugo scrub and coarse sandstone screes. Yaiko Perehinske V.A. Onyshchenko Ukrainian name: Яйко Перегінське. Area: 358.0 ha. Altitude: 1000–1596 m. Latitude: 48°40’03” N (48.6674°). Longitude: 23°54’05” E (23.9014°). Administrative regions. Ivano-Frankivsk region: Rozhniaiv raion. Ownership: state. Biogeographic regions: alpine. Habitats. Level 1. F – 2.4%; G – 95.0%; H – 2.6%. Habitats. Level 2. F2 Arctic, alpine and subalpine scrub – 2.4%; G1 Broadleaved deciduous woodland – 0.5%; G3 Coniferous woodland – 92.0%; G4 Mixed deciduous and coniferous woodland – 2.5%; H2 Screes – 2.5%; H3 Inland cliffs, rock pavements and outcrops – 0.1%. Futher habitat description. F2.4 Conifer scrub close to the tree limit; G1.6 Fagus woodland; G3.1 Abies and Picea woodland; G4.6 Mixed Abies – Picea – Fagus woodland; H2.3 Temperate-montane acid siliceous screes; H3.1 Acid silicious inland clifs. Land use: forestry – major; nature conservation and research – major. Protected areas: includes Yaikivskyi state botanical reserve (270 ha), included in Emerald Site “Dolynsko-Rozhniatynskyi”. Threats: forestry (intensiied forest management) – low. General description. Predominant vegetaion is Picea abies forests with admixture of Pinus cembra. Lower layers are dominated by Vaccinium myrillus, Homogyne alpina, Oxalis acetosella, Calamagrosis arundinacea. Other species of high constancy are Dicranum scoparium, Doronicum 342 Botanical significance. Important area for Carpathian Pinus cembra forests. Criterion C • G3.25 Carpathian Larix and Pinus cembra forests; area: 18 ha; trend: decreasing; area data quality: good; trend data quality: medium. Literature 1. Природно-заповідні території та об’єкти Івано-Франківщини. – Івано-Франківськ, 2000. – 272 с. Yelanetskyi Step V.A. Onyshchenko Ukrainian name: Єланецький степ. Transliteraion/Translaion variants: Yelanets Steppe. Area: 1675.7 ha. Altitude: 30–100 m. Latitude: 47°33’31” N (47.5586°). Longitude: 32°01’27” E (32.0242°). Administrative regions. Mykolaiv region: Yelanets raion, Nova Odesa raion. 343 Habitats. Level 1. E – 98.1%; F – 0.2%; G – 1.5%; H – 0.2% Habitats. Level 2. E1 Dry grasslands – 87.1%; E2 Mesic grasslands – 11.0%; F3 Temperate and mediterranean-montane scrub – 0.2%; G1 Broadleaved deciduous woodland – 1.5%; H3 Inland cliffs, rock pavements and outcrops – 0.02%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.2%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; G1.C Highly ariicial broadleaved deciduous forestry plantaions; I1.5 Bare illed, fallow or recently abandoned arable land. Land use: agriculture (animals) – minor; nature conservaion and research – 100%. Protected areas: same as Yelanetskyi Step nature reserve and Emerald Site “Yelanetskyi Step Nature Reserve”. Threats: –. General description. Valleys of intermitent streams, mainly with the steppe vegetaion. Mesic grasslands occupy botoms of the valleys. There are ourcrops of limestone and granite. Dry grasslands are dominated by Sipa capillata (major), Sipa lessingiana (major), Festuca valesiaca (major), Botriochloa ischaemum (major), Sipa ucrainica, Sipa pulcherrima, Sipa irsa. A signiicant part of steppes (about 75 ha) are co-dominated by Caragana frutex, rarely by other shrub species (Caragana scythica, Chamaecyisus graniicus). Other typical specis of the steppe communiies: Achillea nobilis, Bromopsis riparia, Eryngium campestre, Euphorbia seguierana, Euphorbia stepposa, Koeleria cristata, Koeleria lobata, Marrubium praecox, Securigera varia, Teucrium polium. In petrophyic variant of the steppe, Thymus dimorphus co-dominates. Main species of calcareous outcrops and screes are Thymus dimorphus, Jurinea mulilora, Jurinea brachycephala, Centaurea marschalliana, Koeleria brevis. Dominants of other vegetaion types: mesic grasslands – Elytrigia repens, Poa angusifolia, Bromopsis inermis, reedbed – Phragmites australis, Typha laifolia; shrubs – Crataegus curvisepala s.l., abandoned arable lands – Elytrigia repens, Artemisia absinthium, Cirsium arvense, Melilotus oicinalis, Bunias orientalis. Botanical significance. Important for conservaion of Chamaecyisus graniicus and Tulipa hypanica. One of the best steppe areas west to the Dnipro river. Criterion A • Chamaecyisus graniicus (Rehmann.) Rothm.; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. • Tulipa hypanica Klokov et Zoz; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1300 ha; trend: stable; area data quality: good; trend data quality: good . Literature 1. Бойко М.Ф. Анотований список мохоподібних заповідника “Єланецький степ” та прилеглих територій (Миколаївська область, Україна) // Чорноморськ. бот. журн. – 2009. – 5, № 4. – С. 583–588. 2. Бойко Т.О. Лишайники та ліхенофільні гриби вапнякових відслонень природного заповідника “Єланецький степ” // Чорноморськ. бот. журн. – 2008. – 4, № 1. – С. 84–89. 3. Бойко Т.О. Анотований список лишайників та ліхенофільних грибів природного заповідника “Єланецький степ” // Чорноморськ. бот. журн. – 2009. – 5, № 3. – С. 448–458. 4. Бойко Т.О. Нові та рідкісні для України лишайники з природного заповідника “Єланецький степ” // Чорноморськ. бот. журн. – 2009. – 5, № 2. – С. 241–247. 5. Воронова С.М. Фітораритети судинних рослин міжнародного та державного природоохоронного статусу у природному заповіднику “Єланецький степ” // Вісник Національного науково-природничого музею України. Серія ботанічна. Частина друга. – 2005–2007. – № 4–5. – С. 298–333. 6. Воронова С.М. Раритетний фітофлорофонд та природно-заповідна мережа Єланецько-Інгульського регіону // Заповідна справа в Україні. – 2008. – Т. 14, вип. 1. – С. 66–70. 7. Коломійчук В.П., Мойсієнко І.І., Деркач О.М., Бойко Т.О. ПЗ Єланецький степ // Фіторізноманіття заповідників і національних природних парків України. Ч. 1. Біосферні заповідники. Природні заповідники / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 124–138. 8. Костильов О.В. Рослинність запроектованого заповідника “Єланецький” // Укр. ботан. журн. – 1987. – 44, № 2. – С. 77–81. 9. Костылев А.В. Еланецкий (заповедник) / Перспективная сеть заповедных объектов Украины. – Киев: Наукова думка, 1987. – С. 199–204. 10. Мойсієнко І.І., Соломаха В.А., Драбинюк Г.В., Соломаха Т.Д. Еколого-ценотичні особливості Scutellaria verna Besser в умовах природного заповідника “Єланецький степ” // Чорноморський ботанічний журнал. – 2005. – 1, № 2. – С. 83–91. 11. Ткаченко В.С. Структурні зміни в рослинному покриві “Єланецького степу” за перше десятиліття заповідання // Чорноморський ботанічний журнал. – 2009. – 5, № 3. – С. 319–332. 12. Ткаченко В.С. Зміни ектопічних характеристик заповідника “Єланецький степ” в першому десятилітті його існування // Чорноморський ботанічний журнал. – 2009. – 5, № 4. – С. 475–490. 344 345 Ownership: state. Biogeographic regions: steppic. 13. Ткаченко В.С., Сиротенко П.О. Вихідний стан рослинності “Єланецького степу” в системі фітоценотичного моніторингу // Укр. ботан. журн. – 1999. – 56, № 6. – С. 623–629. Yemilchynski Lisy Ukrainian name: Ємільчинські ліси. Transliteraion/Translaion variants: Yemilchyne Forests. Area: 2645.0 ha. Altitude: 192–203 m. Latitude: 50°59’28” N (50.9911°). Longitude: 27°36’43” E (27.6118°). Administrative regions. Zhytomyr region: Yemilchyne raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. D – 0.6%; F – 0.5%; G – 97.9%; H – 1.0%. 346 O.O. Orlov, V.A. Onyshchenko Habitats. Level 2. D2 – Valley mires, poor fens and transition mires – 0.6%; F9 Riverine and fen scrubs – 0.5%; G1 Broadleaved deciduous woodland – 32.0%; G3 Coniferous woodland – 29.0%; G4 Mixed deciduous and coniferous woodland – 34.2%; G5 Lines of trees, small anthropogenic woodlands, recently felled woodland, early-stage woodland and coppice – 2.7%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. D2.3 Transition mires and quaking bogs; F9.2 Salix carr and fen scrub; G1.5 Broadleaved swamp woodland on acid peat; G1.8 Acidophilous Quercusdominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G3.4 Pinus sylvestris woodland south of the taiga; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland; G5.6 Early-stage natural and semi-natural woodlands and regrowth; H5.6 Trampled areas. Land use: forestry – major; nature conservaion and research – 17%. Protected areas: includes Yuzykhivka regional forest reserve (439 ha). Threats: forestry (intensiied forest management) – medium. General description. Vegetaion is represented by acidophilous Pinus sylvestris, Quercus robur, Betula pendula woods, and Betula pubescens swamps. Dominants of the wet pine woods are Franula alnus, Molinia caerulea, Pteridium aquilinum, Vaccinium myrillus, Dicranum polysetum, Pleurozium shreberi. Other frequent species are Dryopteris carthusiana, Trientalis europaea (Lysimachia europaea), Vaccinium uliginosum, Vaccinium viis-idaea. On the drier soils, there are species rich Pinus sylvestris woods with dominance of Rhododendron luteum in the shrub layer. Dominants of the herb layer are Convallaria majalis and Pteridium aquilinum. Constant species: Calamagrosis arundinacea, Carex montana, Galium intermedium, Maianthemum bifolium, Polygonatum odoratum, Primula veris, Serratula coronata. Diferenial species of the swamped pine woods are Andromeda polifolia, Carex nigra, Ledum palustre, Sphagnum fallax, Sphagnum palustre. In acidophilous Quercus robur woods, there are the shrub layer consising of Frangula alnus. The herb layer is dominanted by Anemone nemorosa, Luzula pilosa, Lysimachia vulgaris, Oxalis acetosella. Dominants of the mesotrophic swamps are Betula pubescens, Carex lasiocarpa, Juncus conglomeratus, Molinia caerulea, Sphagnum fallax. Botanical significance. Important for conservaion of Rhododendron lutem and acidophilous oak forests. Criterion A • Rhododendron luteum Sweet; A(ii); abundance: frequent; trend: stable; species data quality: good; trend data quality: medium. Criterion C • G1.8 Acidophilous Quercus-dominated woodland; area: 800 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Орлов О.О., Сіренький С.П., Якушенко Д.М., Жижин М.П., Степаненко М.А., Тарасевич О.В. Природно-заповідний фонд Житомирської області. Довідник / За заг. ред. О.О. Орлова. – Житомир – Новоград-Волинський: Вид-во НОВОград, 2015. – 404 с. 2. Орлов О.О., Якушенко Д.М., Воробйов Є.О. Флористична класифікація лісів із участю Rhododendron luteum Sweet та радіоекологічна оцінка їх асоціацій в Поліссі України. І. Синтаксономія лісів із участю Rhododendron luteum // Укр. фітоцен. зб. – 2000. - Серія А, Вип. 1 (16). – Київ: Фітосоціоцентр. – С. 94–113. 347 Yulivski Hory R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Юлівські гори. Transliteraion/Translaion variants: Yulivski Gory, Yulivs’ki Hills. Area: 601 ha. Altitude: 129–318 m. Latitude: 48°01’35” N (48.0265°). Longitude: 23°05’06” E (23.0849°). Administrative regions. Zakarpatska region: Vynohradiv raion. Ownership: state. Biogeographic regions: pannonian. biosphere reserve (naional caregory), includes state botanical reserve “Yulivska Hora” (176 ha, belongs to the biosphere reserve), includes regional botanical reserve “Kholmovetska Hora” (95.4 ha), overlaps (176 ha) with Emerald Site “Carpathian Biosphere Reserve”, overlaps (227 ha) with Emerald Site “Okli-Hed”, overlaps (32.4 ha) with proposed regional botanical reserve “Dibrovy Zatysianshchyny”. Threats: abandonment/reducion of land management – low, consequences of invasive species – low, forestry (intensified forest management) – low. General description. Hills composed of tuf, andesite, basalt, and sedimentary rocks. The major vegetaion type is the termophilous oak wood. The tree layer consists of Quercus petraea, Cerasus avium, Carpinus betulus, Acer tataricum, someimes with Quercus dalechampii, Quercus polycarpa, Quercus cerris, Tilia tomentosa. In the shrub layer there are Acer tataricum, Corylus avellana, Crataegus monogyna s. l., Euonymus europaeus, Sambucus nigra, Swida sanguinea (Cornus sanguinea). Typical species of the herb layer are Anthericum ramosum, Brachypodium pinnatum, Campanula persicifolia, Carex michelii, Clinopodium vulgare, Digitalis grandilora, Hieracium murorum, Hylotelephium polonicum, Inula ensifolia, Lathyrus niger, Melittis melissophyllum, Poa nemoralis, Polygonatum odoratum, Potenilla alba, Pyrethrum corymbosum, Veronica teucrium, Vincetoxicum hirundinaria, Viscaria viscosa. In woods on steep southern slopes, there occur Brachypodium pinnatum, Festuca valesiaca, Galium campanulatum, Inula hirta, Phleum phleoides, Poa angusifolia, Stachys recta, Veronica spicata. Besides there are beech forests (with Allium ursinum, Asarum europaeum, Dentaria bulbifera (Cardamine bulbifera), Lamium galeobdolon, Mercurialis perennis, Pulmonaria obscura), oak-hornbeam forests and small areas of dry grasslands (dominated by Festuca rupicola, Festuca pseudodalmaica) and shrubs. Botanical significance. The largest locaion of termophilous oak woods in Transcarpathian part of Ukraine. Criterion C • G1.7 Thermophilous deciduous woodland (*91H0, *91I0, 91M0); area: 400 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Remove alien tree species. Do not allow the expansion of shrubs in grasslands. Create proposed botanical reserve “Dibrovy Zatysianshchyny”. Literature 1. Стойко С.М. Дубові ліси Українських Карпат: екологічні особливості, відтворення, охорона. – Львів, 2009. – 220 с. 2. Фіторізноманіття заповідників і національних природних парків України. Ч.1. Біосферні заповідники. Природні заповідники / Колектив авторів під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – 406 с. Habitats. Level 1. E – 0.3%; F – 0.1%; G – 99.0%; H – 0.6%. Habitats. Level 2. E1 Dry grasslands – 0.3%; F3 Temperate and mediterranean-montane scrub – 0.1%; G1 Broadleaved deciduous woodland – 99.0%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.6%. Futher habitat description. E1.2 Perennial calcareous grassland and basic steppes – 0.3%; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.6 Fagus woodland; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. Land use: forestry – 99%, nature conservation and research – 82%. Protected areas: overlaps (176 ha) with Carpathian biosphere reserve (UNESCO) (includes cluster “Yulivskai Hora” of the biosphere reserve), overlaps (176 ha) with the Karpatskyi V.A. Onyshchenko, O.V. Lukash Ukrainian name: Заплава Десни. Transliteraion/Translaion variants: Floodplain of the Desna River. Area: 185741 ha. Altitude: 95–130 m. Latitude: 51°23’17” N (51.3881°). Longitude: 32°11’12” E (32.1865°). 348 349 Zaplava Desny Administrative regions. Chernihiv region: Borzna raion, Chernihiv city, Chernihiv raion, Kozelets raion, Korop raion, Kulykivka raion, Mena raion, Novhorod-Siverskyi city, NovhorodSiverskyi raion, Sosnytsia raion; Kyiv region: Brovary raion, Vyshhorod raion; Sumy region: Krolevets raion, Shostka raion, Seredyna-Buda raion. Ownership: state, private. Biogeographic regions: continental. Habitats. Level 1. C – 5%; D – 15%; E – 68%; F – 1%; G – 9%; H – 1%; I – 1%. Habitats. Level 2. C1 Surface standing waters – 2%; C2 Surface running waters – 3%; C3 Littoral zone of inland surface waterbodies – 1%; D5 Sedge and reedbeds, normally without free-standing water – 15%; E2 Mesic grasslands – 33%; E3 Seasonally wet and wet grasslands – 35%; E5 Woodland fringes and clearings and tall forb stands – 5.3%; F9 Riverine and fen scrubs – 1%; G1 Broadleaved deciduous woodland – 6%; G3 Coniferous woodland – 3%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%; I1 Arable land and market gardens – 1%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; C3.5 Periodically inundated shores with pioneer and ephemeral vegetation; C3.6 Unvegetated or sparsely vegetated shores with soft or mobile sediments; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E2.1 Permanent mesotrophic pastures and aftermath-grazed meadows; E2.2 Low and medium alitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E5.4 Moist or wet tall-herb and fern fringes and meadows; F9.1 Riverine scrub; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G3.4 Pinus sylvestris woodland south of the taiga. Land use: agriculture (animals) – 15%; agriculture (arable) – 1%; forestry – 9%; mowing/hay making – 45%; nature conservation and research – 5%; urban/industrial/transport – minor. Protected areas: overlaps (3743 ha) with Desniansko-Starohutskyi national nature park, overlaps (14038 ha) with Desnianskyi biosphere reserve, overlaps (about 5007 ha) with Mezynskyi national nature park, overlaps with Mizhrichynskyi regional landscape park (about 11200 ha), includes Desna River Floodplains Ramsar Site (4270 ha), includes Kamoretskyi state zoological reserve (515 ha), Obolonskyi state botanical reserve (400 ha), Putyvskyi state botanical reserve (150 ha), Muravyivska state hydrological nature monument (40 ha), Ozero Trubyn state hydrological nature monument (40 ha), Vaden’ state hydrological nature monument (20 ha), includes Babakove regional hydrological reserve (12 ha), Boloto Kolodlyve regional hydrological reserve (13.3 ha), Blystovskyi regional landscape reserve (400 ha), Deminka regional landscape reserve (1431 ha), Fedorove regional hydrological reserve (14 ha), Horytskyi landscape hydrological reserve (796 ha), Kovchynskyi regional landscape reserve (311 ha), Kyslyche regional hydrological reserve (178 ha), Lebedynske regional hydrological reserve (184 ha), Makoshynskyi regional landscape reserve (1533 ha), Mialyne regional hydrological reserve (102 ha), Oryvtsiove regional hydrological reserve (12 ha), PaikaKryvcha regional hydrological reserve (216 ha) Popovychove regional hydrological reserve (11 ha), Smolianske regional hydrological reserve (15 ha), Spaskyi regional landscape reserve (543 ha), Spaskyi–1 regional hydrological reserve (214 ha), Synychne regional hydrological reserve (10 ha), Urochyshche Kuty regional botanical reserve (122 ha), Vuzke regional hydrological reserve (11 ha), Zadesniansly regional landscape reserve (940 ha), Zolotynka regional landscape reserve (527 ha), includes Ramsar Site “Desna river loodplains” (4270 ha), includes proposed Ramsar Site “Floodplains between town Oster and village Smolyn”, overlaps (82511 ha) with Emerald Site “Chernihivske Podesennia”, overlaps (3743 ha) with Emerald Site “Desniansko-Starohutskyi Naional Nature Park”, overlaps (14038 ha) with Emerald Site “Desnianskyi Biosphere Reserve”, overlaps overlaps (5340 ha) with Emerald Site “Kyivske Podesennia”, overlaps (13660 ha) with Emerald Site “Verhnie Podesennia”, overlaps (5007 ha) with Emerald Site “Mezynskyi Naional Nature Park”, overlaps (1824 ha) with Emerald Site “Dolyna Seimu”, overlaps (50750 ha) with Emerald Site “Nyzhnie Podesennia”, overlaps (7058 ha) with Emerald Site “Mizhrichynskyi Regional Landscape Park”, overlaps with proposed naional nature parks “Prydesnianskyi” and “Shostkynskyi”. Threats: abandonment/reduction of land management – low, agricultural intensification/ 350 351 expansion (general) – low; burning of vegetation – low, development (urbanization) – low, water (drainage) – low. General description. 338 km section of the floodplain of the Desna river. This is the largest floodplain with natural water regime in Ukraine. Its average width is about 5 km. Floods are regular. The riverbed has natural meanders. There are many oxbows and lakes. Major vegetation types are mesic meadows dominated by Alopecurus pratensis, Poa pratensis, Festuca pratensis, Festuca rubra, Agrostis gigantea; drier sandy meadows dominated by Poa angustifolia, Agrostis vinealis, Calamagrostis epigeios; moist medadows dominated by Deschampsia cespitosa, Phalaroides arundinacea, Filipendula ulmaria, Geranium palustre; mires and littoral vegetation dominated by Phragmites auistralis, Glyceria maxima, Carex acuta, Carex acuiformis, Carex appropinquata, Carex juncella, Carex elata, Carex rostrata, Carex vesicaria, Carex vulpina. There are forests (Salix alba, Quercus robur, Alnus glutinosa, Populus nigra, Populus alba, Pinus sylvestris) and shrubs (Salix cinerea, Salix triandra, Salix acutifolia). Aquatic vegetation is very diverse. Main dominants are Ceratophyllum demersum, Lemna minor, Lemna trisulca, Hydrocharis morsus-ranae, Nuphar lutea, Nymphaea alba, Nymphaea candida, Potamogeton natans, Sagittaria sagittifolia, Sparganium emersum, Stratiotes aloides, Utricualaria vulgaris. Botanical significance. This area is most important for conservation of floodplain complexes in Ukraine. Criterion C • C1.223 Floating Stratiotes aloides rafts; area: 30 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.224 Floating Utricularia australis and Utricularia vulgaris colonies; area: 20 ha; trend: stable; area data quality: poor; trend data quality: medium. • C1.3411 Ranunculus communities in shallow water; area: 1 ha; trend: stable; area data quality: poor; trend data quality: medium. • C2.33 Mesotrophic vegetation of slow-flowing rivers; area: 200 ha; trend: stable; area data quality: poor; trend data quality: medium. • C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation ; area: 30 ha; trend: stable; area data quality: poor; trend data quality: medium. • C3.51 Euro-Siberian dwarf annual amphibious swards; area: 30 ha; trend: stable; area data quality: poor; trend data quality: medium. • D5.2 Beds of large sedges normally without free-standing water; area: 25000 ha; trend: stable; area data quality: poor; trend data quality: medium. • E2.2 Low and medium alitude hay meadows; area: 30000 ha; trend: stable; area data quality: medium; trend data quality: medium. • E3.4 Moist or wet eutropic and mesotrophic grassland; area: 65000 ha; trend: stable; area data quality: medium; trend data quality: medium. • E3.5 Moist or wet oligotrophic grassland; area: 1000 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.4 Moist or wet tall-herb and fern fringes and meadows; area: 300 ha; trend: stable; area data quality: poor; trend data quality: poor. • F9.1 Riverine scrub; area: 5000 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.11 Riverine Salix woodland; area: 2000 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.21 Riverine Fraxinus – Alnus woodland, wet at high but not at low water; area: 200 352 ha; trend: stable; area data quality: poor; trend data quality: poor. G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: poor. Conservaion proposals. Сreate Emerald Sites including the enire IPA. Literature 1. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 216 с. 2. Водно-болотні угіддя України / Під ред. Г.Б. Марушевського, І.С. Жарук. – К.: Wetlands International Black Sea Programme, 2006. – 312 с. 3. Деснянський екологічний коридор / під заг. ред. В.Костюшина, Є.Прекрасної. – К.: НЕЦУ, 2010. – 164 с. 4. Карпенко О.Ю. НПП Мезинський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 312–320. 5. Панченко С.М. НПП Деснянсько-Старогутський // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 215–229. 6. Панченко С.М., Андрієнко Т.Л., Гаврись Г.Г., Кузьменко Ю.В. Екологічна мережа Новгород-Сіверського Полісся. – Суми: Університетська книга, 2003. – 92 с. 7. Перспективная сеть заповедных объектов Украины / под ред. Ю.Р.ШелягСосонко. – К.: Наук. думка, 1987. – 292 с. 8. Смарагдова мережа в Україні / Колектив авторів під ред. Проценка Л.Д. – Київ: Хімджест, 2011. – 192 с. • Zaplava Latorytsi V.A. Onyshchenko Ukrainian name: Заплава Латориці. Transliteraion/Translaion variants: Floodplain of the Latorytsa River. Area: 4752 ha. Altitude: 99–110 m. Latitude: 48°27’54” N (48.4649°). Longitude: 22°21’15” E (22.3541°). Administrative regions. Zakarpatska region: Uzhhorod raion, Mukachevo raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. C – 2.3%; D – 1.5%; E – 22.0%; F – 6.0%; G – 68.2%. Habitats. Level 2. C1 Surface standing waters – 0.8%; C2 Surface running waters – 0.9%; C3 Littoral zone of inland surface waterbodies – 0.6%; D5 Sedge and reedbeds, normally without free-standing water – 1.5%; E3 Seasonally wet and wet grasslands – 22.0%; F9 Riverine and fen scrubs – 6.0%; G1 Broadleaved deciduous woodland – 68.2%. Futher habitat descripion. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.5 Periodically inundated shores with pioneer and ephemeral vegetation; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E3.4 353 Moist or wet eutrophic and mesotrophic grassland; F9.1 Riverine scrub; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Land use: agriculture (animals) – minor, forestry – 50%; mowing/hay making – minor, nature conservation and research – major. Protected areas: overlaps (about 4752 ha) with Prytysianskyi regional landscape park, includes Velykodobronskyi state zoological reserve (1736 ha), overlaps (about 4493 ha) with Emerald Site “Prytysianskyi”. Threats: –. General description. A part of the loodplain of the Latorytsia river. Moist Fraxinus pannonica and Quercus robur forest occupies about half of the territory. There is also a large area of wet meadows. Botanical significance. Important area for loodplain ash-oak forests. Criterion C • G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 3000 ha; trend: stable; area data quality: medium; trend data quality: poor. Literature 1. Регіональний ландшафтний парк “Притисянський” – збереження природної спадщини рівнинного Закарпаття / Р. Кіш, Б. Проць, А. Поляновський, Т. Башта та ін.. – Ужгород: Мистецька лінія, 2009. – 20 с. 354 Zaplava Prypiai V.A. Onyshchenko Ukrainian name: Заплава Прип’яті. Transliteraion/Translaion variants: Floodplain of the Prypiat’ (Pripet) River. Area: 44488 ha. Altitude: 137–154 m. Latitude: 51°51’59” N (51.8664°). Longitude: 25°25’08” E (25.4188°). Administrative regions. Rivne region: Zarichne raion; Volynska region: Liubeshiv raion, Ratno raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. C – 3.5%; D – 59%; E – 15%; F – 13%; G – 9%; I – 0.5%. Habitats. Level 2. C1 Surface standing waters – 3%; C2 surface running waters – 0.1%; C3 littoral zone of inland surface waterbodies – 0.4%; D2 Valley mires, poor fens and transition mires – 10%; D5 Sedge and reedbeds, normally without free-standing water – 49%; E2 Mesic grasslands – 3%; E3 Seasonly wet and wet grasslands – 12%; F9 Riverine and fen scrubs – 13%; G1 Broadleaved deciduous woodland – 6%; G3 Coniferous woodland – 1%; G4 Mixed deciduous and coniferous woodland – 2%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-lowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D2.2 Poor fens and sot-water spring mires; D2.3 Transiion mires and quaking bogs; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E1.9 Open non-Mediterranean dry acid and neutral grassland including inland dune grassland; E2.1 Permanent mesotrophic pastures and aftermath-grazed meadows; E2.2 Low and medium altitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; E3.5 Moist or wet oligotrophic grassland; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant 355 Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.5 Broadleaved swamp woodland on acid peat; G1.7 Thermophilous deciduous woodland; G1.8 Acidophilous Quercusdominated woodland; G1.9 Non-riverine woodland with Betula, Populus tremula or Sorbus aucuparia; G1.B Non-riverine Alnus woodland; G3.4 Pinus sylvestris woodland south of the taiga; G4.4 Mixed Pinus sylvestris – Betula woodland; G4.7 Mixed Pinus sylvestris – acidophilous Quercus woodland. Land use: forestry – minor, nature conservation and research – 71%. Protected areas: overlaps (about 26400 ha) with Prypiat-Stokhid naional nature park; overlaps (about 11300 ha) with Prypiat-Stokhid regional landscape park (Rivne region); overlaps (about 23400 ha) with Ramsar site “Prypiat river loodplains”, includes Birkivskyi regional hydrological reserve (850 ha), Hirkivskyi regional hydrological reserve (400 ha), Zalukhivskyi regional hydrological reserve (839 ha), Velykohlushanskyi regional hydrological reserve (360 ha), Vetlivskyi regional hydrological reserve (850 ha), Nobelskyi regional ornithological reserve (510 ha), Prypiatski regional ichthyological reserve (3155 ha), regional hydrological reserve “Prypiatskyi–1” (340 ha), regional hydrological reserve “Prypiatskyi–2” (220 ha), regional hydrological reserve “Prypiatskyi–3” (320 ha), Tsyrskyi regional hydrological reserve (210 ha), overlaps (about 26817 ha) with Emerald Site “PrypiatStokhid Naional Nature Park”, overlaps (about 9664 ha) with Emerald Site “ Stokhid-Nobel”. Threats: –. General description. The loodplain of the Prypiat river with fragments of a higher terrace. The area includes lakes Liubiaz (430 ha), Nobel (470 ha), Volianske (405 ha). Eutrophic sedge mires occupy the largest area. Main dominants are Carex appropinquata and Carex elata, other typical species are Potenilla palustris, Lythrum salicaria, Thelypteris palustris, Iris pseudacorus. Large areas are covered by Alnus gluinosa and Salix cinerea swamps. There occur poor fens with Carex nigra, Carex panicea, Carex lava, Agrosis canina. Floodplain meadows are dominated mainly by Deschampsia cespitosa, Molinia caerulea, someimes by Agrosis capillaris, Poa pratensis, Agrosis stolonifera. The most typical dominants of aquaic vegetaion are Straiotes aloides, Potamogeton nodosus, Potamogeton lucens. Main dominants of the litoral vegetaion are Phragmites australis, Typha angusifolia, Glyceria maxima. Pinus sylvestris and Quercus robur forests on the sand terrace are dominated by Vaccinium myrillus, Pteridium aquilinum, Molinia caerulea. There are several areas od sand dunes. There are complexes of unvegetated sands with communiies of Corynephorus canescens (predominanly), Calamagrosis epigeios, Koeleria glauca, Filago minima, Polytrichum piliferum with presence of Centaurea stoebe, Helichrysum arenarium, Thymus serpyllum. Botanical significance. The IPA includes the largest eutrophic sedge mire in Ukraine, important for conservaion of Aldrovanda vesiculosa. Criterion A • Aldrovanda vesiculosa L.; A(i), A(ii); abundance: occasional; trend: unknown; species data quality: medium; trend data quality: poor. Criterion C • C1.223 Floating Stratiotes aloides rafts; area: 50 ha; trend: stable; area data quality: poor; trend data quality: poor. • C1.226 Floating Aldrovanda vesiculosa communities; area: <0.1 ha; trend: unknown; area data quality: poor; trend data quality: poor. • D5.2 Beds of large sedges normally without free-standing water; area: 15000 ha; trend: stable; area data medium: poor; trend data quality: poor. 356 • E3.4 Moist or wet eutropic and mesotrophic grassland; area: 5000 ha; trend: stable; area data quality: medium; trend data quality: medium. • E3.5 Moist or wet oligotrophic grassland; area: 1000 ha; trend: stable; area data quality: poor; trend data quality: poor. • X35 Inland sand dunes; area: 38 ha; trend: stable; area data quality: medium; trend data quality: medium. Literature 1. Андрієнко Т.Л., Прядко О.І. Флористичне та ценотичне різноманіття проектованого національного природного парку “Прип’ять-Стохід” // Науковий вісник Волинського державного університету імені Лесі Українки. І Міжнародна науково-практична конференція “Шацький національний природний парк: регіональні аспекти, шляхи та напрями розвитку”. – 2007. – 11, ч. 2. – С. 132–140. 2. Андрієнко Т.Л., Прядко О.І. НПП Прип’ять-Стохід // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 429–439. 3. Андрієнко Т.Л., Прядко О.І., Арап Р.Я., Коніщук М.О. Національний природний парк “Прип’ять-Стохід”. Рослинний світ / Під заг. ред. Т.Л.Андрієнко. – К.: Фітосоціоцентр, 2009. – 86 с. 4. Прядко О.І. Рослинний покрив водно-болотних угідь РЛП “Прип’ять-Стохід” // Сучасний стан водно-болотних угідь регіонального ландшафтного парку “Прип’ятьСтохід” та їх біорізноманіття. – К:, 2001 – С. 70–75. Zaplava Siverskoho Dintsia V.A. Onyshchenko Ukrainian name: Заплава Сіверського Дінця. Transliteraion/Translaion variants: Floodplain of the Siverskyi Donets’ River. Area: 16679 ha. Altitude: 49–70 m. Latitude: 48°54’07N (48.9020°). Longitude: 37°50’05” E (37.8347°). Administrative regions. Donetsk region: Sloviansk raion, Lyman (Krasnyi Lyman) raion; Luhansk region: Kreminna raion. Ownership: state. Biogeographic regions: steppic Habitats. Level 1. C – 6.8%; D – 1.9%; E – 20.9%; G – 69.9%; H – 0.5%. Habitats. Level 2. C1 Surface standing waters – 2.6%; C2 Surface running waters – 3.6%; C3 Littoral zone of inland surface waterbodies – 0.6%; D5 Sedge and reedbeds, normally without free-standing water – 1.9%; E2 Mesic grasslands – 19.0%; E3 Seasonally wet and wet grasslands – 1.9%; G1 Broadleaved deciduous woodland – 68.6%; G3 Coniferous woodland – 1.2%; G4 Mixed deciduous and coniferous woodland – 0.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.5%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.2 Mixed riparian floodplain and gallery woodland; G1.3 Mediterranean riparian woodland; G1.4 Broadleaved swamp woodland not on acid 357 peat; G3.4 Pinus sylvestris woodland south of the taiga; G4.C Mixed Pinus sylvestris – thermophilous Quercus woodland; H5.6 Trampled areas. Land use: agriculture (animals) – 10%; mowing/hay making – 25%; forestry – 70%; nature quality: medium; trend data quality: medium. Literature 1. Бурда Р.І., Остапко В.М., Глухов А.З., Шпилева Н.В. Національний природний парк “Святі Гори”: біологічна різноманітність рослинного покриву // Заповідна справа в Україні. – 1997. – Т. 3, вип.1. – С.10–17. 2. Морозова І. Міксоміцети Національного природного пароку “Святі Гори” // Матли ІV Міжн. наук. конф. студентів та аспірантів “Молодь і поступ біології” (м. Львів, 7–10 квітня 2008 р.). – Львів: ЛНУ ім. І. Франка, 2008. – С.106–107. 3. Надєіна О.В. Лишайники національного природного парку “Святі Гори” // Чорноморський ботан. журн. – 2007. – 3, № 2. – С. 100–108. 4. Остапко В.М., Шпилева Н.В., Дьякова О.В. НПП Святі гори // Фіторізноманіття заповідників і національних природних парків України. Ч. 2. Національні природні парки / під ред. В.А. Онищенка і Т.Л. Андрієнко. – Київ: Фітосоціоцентр, 2012. – С. 440–456. Zaplava Tysy conservaion and research – 34%. Protected areas: overlaps (about 7403 ha) with Sviai Hory naional nature park and Emerald Site “Sviai Hory “, overlaps with Emerald Site “Kreminski Lisy” (5252 ha). Threats: agricultural intensiicaion/expansion (general) – low; development (recreaion/ tourism) – low; forestry (intensified forest management) – low. General description. The loodplain of the Siverskyi Donets river. Its major vegetaion is represented by broadleaved forests and meadows. The largest area is occupied by Quercus robur forests with co-domimanance of Tilia cordata, Populus tremula, Fraxinus excelsior. Other typical species are Euonymus europaeus, E. verrucosus, Corylus avellana, Crataegus avellana, Acer tataricum, Aegopodium podagraria (dominant), Convallaria majalis (dominant), Stellaria holostea (dominant), Anemone ranunculoides, Corydalis solida, Ficaria verna, Glechoma hederacea, Lysimachia nummularia, Pulmonaria obscura, Scilla siberica, Tulipa quercetorum, Viola odorata, Viola mirabilis. Besides there occur Alnus gluinosa and Populus alba forests. Floodplain meadows are dominated by Festuca pratensis, Elytrigia repens, Koeleria delavignei, Phleum pratense, Poa pratensis. Dominants of eutrophic mires are Phragmites australis (major), Carex acuta, Carex acutiformis, Carex riparia, Carex vesicaria. Dominants of litoral vegetaion: Phragmites australis, Acorus calamus, Schoenoplectus lacustris, Typha angustifolia, Typha latifolia. Dominants of aquaic vegetaion: Lemna minor, Potamogeton natans, Nuphar lutea, Nymphaea alba, Salvinia natans. Botanical significance. Important for conservaion of Quercus robur loodplain forests, black alder woods and loodplain meadows. Criterion C • E2.2 Low and medium alitude hay meadows; area: 2700 ha; trend: stable; area data quality: good; trend data quality: medium. • G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 9000 ha; trend: stable; area data quality: medium; trend data quality: medium. • G1.3 Mediterranean riparian woodland; area: 140 ha; trend: unknown; area data quality: poor; trend data quality: poor. • G1.414 Steppe swamp Alnus gluinosa woods; area: 700 ha; trend: stable; area data 358 R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Заплава Тиси. Transliteraion/Translaion variants: Floodplain of the Tysa (Tisza) River. Area: 7930 ha. Altitude: 115–204 m. Latitude: 48°11’03N (48.1841°). Longitude: 23°10’57” E (23.1823°). Administrative regions. Zakarpatska region: Khust city, Khust raion, Tiachiv raion, Vynohradiv raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. C – 20.0%; D – 3.0%; E – 16.0%; F – 3.0%; G – 57.0%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 0.3%; C2 Surface running waters – 7.7%; 359 C3 Littoral zone of inland surface waterbodies – 12.0%; D5 Sedge and reedbeds, normally without free-standing water – 3.0%; E2 Mesic grasslands – 2.0%; E3 Seasonally wet and wet grasslands – 14.0%; F9 Riverine and fen scrubs – 3.0%; G1 Broadleaved deciduous woodland – 57.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.3 Permanent eutrophic lakes, ponds and pools; C2.2 Permanent non-tidal, fast, turbulent watercourses; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.6 Unvegetated or sparsely vegetated shores with soft or mobile sediments; E3.4 Moist or wet eutrophic and mesotrophic grassland; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; H5.6 Trampled areas; G1.A Meso- and eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland. Land use: agriculture (animals) – minor; forestry – minor; mowing/hay making – minor; nature conservaion and research – minor; tourism/recreaion – minor. Protected areas: overlaps (about 4596 ha) with Prytysianskyi regional landscape park, includes Ehresh regional botanical reserve (37.4 ha), overlaps (4669 ha) with Emerald Site “Vynohradivska Tysa”. Threats: construcion/impact of dike/dam/barrage – low; eutrophicaion – low. General description. Floodplain of the Tysa river. Vegetaion is represented by Salix alba and Populus nigra forests, Salix shrubs, moist and mesic grasslands. Signiicant parts of total area are running waters and unvegetated alluvial deposits (pebble, gravel). Besides there are standing waters, Alnus gluinosa swamps, sedge beds. Water is predominantly eutrophic. Botanical significance. Important for loodplain forests, shrubs, aquaic and ephemeral litoral vegetaion. Criterion C • C2.34 : Eutrophic vegetaion of slow-lowing rivers; area: 5 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C2.28 : Eutrophic vegetaion of fast-lowing streams; area: 3 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetaion; area: 10 ha; trend: unknown; area data quality: poor; trend data quality: poor. • C3.51 Euro-siberian dwarf annual amphibious swards (but excluding C3.5131 Toad-rush swards); area: 10 ha; trend: unknown; area data quality: poor; trend data quality: poor. • E5.4 Moist or wet tall-herb and fern fringes and meadows; area: 50 ha; trend: unknown; area data quality: poor; trend data quality: poor. • G1.11 Riverine Salix woodland; area: 600 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.3 Mediterranean riparian woodland; area: 3000 ha; trend: unknown; area data quality: poor; trend data quality: poor. 360 Zaplavni Lisy na Borzhavi R.Ya. Kish, V.A. Onyshchenko Ukrainian name: Заплавні ліси на Боржаві. Transliteraion/Translaion variants: Floodplain Forests on the Borzhava. Area: 2775 ha. Altitude: 113–130 m. Latitude: 48°13’00” N (48.2166°). Longitude: 22°48’13” E (22.8034°). Administrative regions. Zakarpathia region: Berehove raion, Vynohradiv raion. Ownership: state. Biogeographic regions: pannonian. Habitats. Level 1. C – 0.3%; D – 0.2%; E – 1.8%; F – 0.0%; G – 97.0%; H – 0.7%. Habitats. Level 2. C1 Surface standing waters – 0.2%; C2 Surface running waters – 0.1%; C3 Littoral zone of inland surface waterbodies – 0.0%; D5 Sedge and reedbeds, normally without free-standing water – 0.2%; E2 Mesic grasslands – 0.1%; E3 Seasonally wet and wet grasslands – 1.7%; F9 Riverine and fen scrubs – 0.0%; G1 Broadleaved deciduous woodland – 97.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 0.7%. Futher habitat description. F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G1.A Mesoand eutrophic Quercus, Carpinus, Fraxinus, Acer, Tilia, Ulmus and related woodland; H5.6 Trampled areas. 361 Land use: forestry – major, nature conservation and research – minor. Protected areas: overlaps (2506 ha) with Prytysianskyi regional landscape park, includes regional preserve (“zapovidne urochyshche”) “Borzhava” (153 ha, included in the regional landscape park), includes regional botanical reserve “Velykyi Lis” (1.5 ha, included in regional preserve “Borzhava”), overlaps (2152 ha) with Emerald Site “Ponyzzia Borzhavy”. Threats: forestry (intensiied forest management) – low. General description. Major vegetaion types are moist loodplain Quercus robur - Fraxinus pannonicus forest and mesic Quercus robur - Carpinus betulus forest. Dominants of the herb layer of the moist forests are Filipendula ulmaria, Glechoma hederacea, Impaiens nolitangere, Phalaroides arundinacea, Rubus caesius, Urica dioica. In the mesic forests, there prevail Anemone nemorosa, Aegopodium podagraria, Hedera helix, Lamium galeobdolon. Besides there are Alnus gluinosa wet forests and Alnus gluinosa swamps, small areas of Salix alba and Salix fragilis woods, sedge and reedbeds, Salix cinerea swamps, meadows. Botanical significance. One of the best riverine forests in Ukraine and Central Europe. Criterion C • G1.22 Mixed Quercus – Ulmus – Fraxinus woodland of great rivers; area: 1400 ha; trend: stable; area data quality: medium; trend data quality: medium • G1.414 Steppe swamp Alnus gluinosa woods; area: 40 ha; trend: stable; area data quality: medium; trend data quality: medium. Conservaion proposals. Stop clear felling and create a state botanical reserve including the enire IPA. pioneer and ephemeral vegetation; F9.1 Riverine scrub; F9.2 Salix carr and fen scrub; G1.1 Riparian and gallery woodland, with dominant Alnus, Betula, Populus or Salix; G1.2 Mixed riparian floodplain and gallery woodland; G1.4 Broadleaved swamp woodland not on acid peat; G3.4 Pinus sylvestris woodland south of the taiga. Zaplavy Dnipra i Sozha V.A. Onyshchenko, O.V. Lukash Ukrainian name: Заплави Дніпра і Сожа. Transliteraion/Translaion variants: Floodplain of the Dnipro and the Sozh. Area: 34967 ha. Altitude: 104–120 m. Latitude: 51°43’50” N (51.7304°). Longitude: 30°39’05” E (30.6515°). Administrative regions. Chernihiv region: Chernihiv raion, Ripky raion. Ownership: state, private. Biogeographic regions: continental Habitats. Level 1. C – 11%; D – 15%; E – 44%; F – 8%; G – 22%. Habitats. Level 2. C1 Surface standing waters – 3.0%; C2 Surface running waters – 7.2%; C3 Littoral zone of inland surface waterbodies – 0.8%; D5 Sedge and reedbeds, normally without free-standing water – 15%; E3 Seasonally wet and wet grasslands – 44%; F9 Riverine and fen scrubs – 8%; G1 Broadleaved deciduous woodland – 18%; G3 Coniferous woodland – 4%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C1.6 Temporary lakes, ponds and pools; C2.3 Permanent non-tidal, smooth-flowing watercourses; C3.2 Water-fringing reedbeds and tall helophytes other than canes; C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; C3.6 Unvegetated or sparsely vegetated shores with soft or mobile sediments; D5.1 Reedbeds normally without freestanding water; D5.2 Beds of large sedges normally without free-standing water; E3.4 Moist or wet eutrophic and mesotrophic grassland; C3.5 Periodically inundated shores with 362 Land use: agriculture (animals) – 10%; agriculture (arable) – 1%; forestry – 20%; mowing / hay making – 30%; nature conservation and research – minor%. Protected areas: includes regional hydrological reserve “Kryvi Hriady” (129.2 ha), includes regional zoological reserve “Kryvi Hriady – 2” (7 ha), includes regional hydrological reserve “Ozera Sympol, Sviate ta Prylehli Bolota” (140 ha), includes regional hydrological reserve “Urochyshche Dor” (166 ha), overlaps (6679 ha) with Emerald Site “Ripkynskyi”, overlaps 363 (6406 ha) with Emerald Site “Liubetskyi”, overlaps (3840 ha) with Emerald Site “Pakulskyi”, overlaps with proposed Liubechskyi national nature park, overlaps with proposed Dniprovskyi naional nature park. Threats: abandonment/reduction of land management – low, agricultural intensification/ expansion (general) – low; burning of vegetation – low, development (urbanization) – low. General description. Ukrainian part of the floodplains of the Dnipro and Sozh rivers length of 104 km. Western boundary runs along the state border between Ukraine and Belarus. This is one of the largest floodplains with natural water regime in Ukraine. Floods are regular. The riverbed has natural meanders. There are many oxbows and lakes. Meadows occupy the largest area. Sandy meadows on high elements of relief are dominated by Calamagrostis epigeios, Agrostis vinealis, Poa angustifolia. Dominants of meadows of a lower level are Alopecurus pratensis, Poa pratensis, Festuca pratensis, Festuca rubra, Agrostis gigantea. Moist meadows are dominated by Deschampsia cespitosa and Phalaroides arundinacea. Mires and littoral vegetation are dominated by Phragmites auistralis, Glyceria maxima, Carex acuta, C. elata, Carex juncella, C. appropinquata. There are forests (Quercus robur, Alnus glutinosa, Salix alba, Pinus sylvestris) and shrubs (Salix cinerea, Salix triandra, Salix acutifolia). Main dominants of aquatic vegetation are Lemna minor, Spirodela polyrrhiza, Sagittaria sagittifolia, Hydrocharis morsus-ranae, Nuphar lutea, Nymphaea alba, Potamogeton perfoliatus, Potamogeton lucens, Stratiotes aloides. Botanical significance. This area is important for conservation of floodplain complexes in Ukraine. Criterion C • C1.223 Floating Stratiotes aloides rafts; area: 6 ha; trend: stable; area data quality: poor; trend data quality: poor. • C1.224 Floating Utricularia australis and Utricularia vulgaris colonies; area: 4 ha; trend: stable; area data quality: poor; trend data quality: poor • C1.3411 Ranunculus communities in shallow water; area: 0.2 ha; trend: stable; area data quality: poor; trend data quality: poor. • C2.33 Mesotrophic vegetation of slow-flowing rivers; area: 80 ha; trend: stable; area data quality: poor; trend data quality: poor. • C3.4 Species-poor beds of low-growing water-fringing or amphibious vegetation; area: 6 ha; trend: stable; area data quality: poor; trend data quality: poor. • C3.51 Euro-Siberian dwarf annual amphibious swards; area: 6 ha; trend: stable; area data quality: poor; trend data quality: poor. • D5.2 Beds of large sedges normally without free-standing water; area: 5000 ha; trend: stable; area data quality: poor; trend data quality: poor. • E2.2 Low and medium alitude hay meadows; area: 5000 ha; trend: stable; area data quality: medium; trend data quality: medium. • E3.4 Moist or wet eutropic and mesotrophic grassland; area: 10000 ha; trend: stable; area data quality: medium; trend data quality: medium. • E3.5 Moist or wet oligotrophic grassland; area: 100 ha; trend: stable; area data quality: poor; trend data quality: poor. • E5.4 Moist or wet tall-herb and fern fringes and meadows; area: 6 ha; trend: stable; area data quality: poor; trend data quality: poor. • F9.1 Riverine scrub; area: 5000 ha; trend: stable; area data quality: poor; trend data quality: poor. • G1.11 Riverine Salix woodland; area: 1000 ha; trend: stable; area data quality: poor; trend data quality: poor. 364 • G1.21 Riverine Fraxinus – Alnus woodland, wet at high but not at low water; area: 150 ha; trend: stable; area data quality: poor; trend data quality: poor. Literature 1. Андриенко Т.Л., Шеляг-Сосонко Ю.Р. Растительный мир Украинского Полесья в аспекте его охраны. – Киев: Наук. думка, 1983. – 216 с. 2. Водно-болотні угіддя України / Під ред. Г.Б. Марушевського, І.С. Жарук. – К.: Wetlands International Black Sea Programme, 2006. – 312 с. 3. Лукаш А.В., Андриенко Т.Л. Ботанически ценные охраняемые природные территории Полесья. – Чернигов: Десна Полиграф, 2014. – 104 с. 4. Перспективная сеть заповедных объектов Украины / под ред. Ю.Р.ШелягСосонко. – К.: Наук. думка, 1987. – 292 с. 5. Смарагдова мережа в Україні / Колектив авторів під ред. Проценка Л.Д. – Київ: Хімджест, 2011. – 192 с. Zelena Balka V.A. Onyshchenko Ukrainian name: Зелена Балка. Transliteraion/Translaion variants: Green Ravine. Area: 1339.0 ha. Altitude: 40–104 m. Latitude: 47°47’29” N (47.7914°). Longitude: 33°11’30” E (33.1915°). Administrative regions. Dnipropetrovsk region: Shyroke raion. Ownership: state. Biogeographic regions: steppic. Habitats. Level 1. C – 3.8%; D – 0.5%; E – 93.7%; F – 0.1%; G – 0.9%; H – 1.0%. Habitats. Level 2. C1 Surface standing waters – 3.4%; C3 Littoral zone of inland surface waterbodies – 0.4%; E1 Dry grasslands – 92.1%; E2 Mesic grasslands – 0.5%; E5 Woodland fringes and clearings and tall forb stands – 0.1%; E7 Sparsely wooded grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 0.1%; G1 Broadleaved deciduous woodland – 0.9%; H2 Screes – 0.0%; H3 Inland cliffs, rock pavements and outcrops – 0.0%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat description. C1.2 Permanent mesotrophic lakes, ponds and pools; C3.2 Water-fringing reedbeds and tall helophytes other than canes; D5.1 Reedbeds normally without free-standing water; E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G1.C Highly ariicial broadleaved deciduous forestry plantaions; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland clifs; H5.6 Trampled areas. Land use: agriculture (animals) – major. Protected areas: –. Threats: –. General description. Grasslands dominated by Festuca valesiaca, Sipa capillata, S. lessingiana, Botriochloa ischaemum, Koeleria cristata, Sipa ucrainica (rarely) with presence of Teucrium polium, Euphorbia seguierana, Euphorbia stepposa, Salvia nutans, Eryngium 365 campestre, Marrubium praecox, Veronica barellieri, Artemisia austriaca, Medicago falcata. In more mesic habitats, there prevail Poa angusifolia, Bromopsis inermis, Elytrigia intermedia, Elytrigia trichophora, Carex praecox, frequent species are Achillea pannonica, Marrubium Criterion A • Chamaecyisus graniicus (Rehmann.) Rothm.; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: medium. • Tulipa hypanica Klokov et Zoz; A(iii); abundance: occasional; trend: stable; species data quality: medium; trend data quality: poor. Criterion C • E1.2 Perennial calcareous grassland and basic steppes; area: 1000 ha; trend: stable; area data quality: medium; trend data quality: good. Conservaion proposals. Create a state reserve and an Emerald Site.. Literature 1. Красова О.О., Сметана О.М. Матеріали до оцінки перспективних степових компонентів екомережі Кривбасу (“Балка Зелена”) // Чорноморський ботанічний журнал. – 2012. – 8, № 4. – С. 459–470. Zholoby H.I. Oliiar, H.P. Protsiv Ukrainian name: Жолоби. Area: 60.0 ha. Altitude: 308–387 m. Latitude: 49°29’04” N (49.4845°). Longitude: 24°53’20” E (24.8888°). praecox, Galium ruthenicum, Plantago urvillei. In shrub steppes, Amygdalus nana, Caragana frutex, Caragana scythica predominate. On stony calcareous soil, there prevail Jurinea brachycephala, Teucrium chamaedrys, Potenilla incana, Sipa asperella, Galatella villosa, Elytrigia sipifolia, Chamaecyisus graniicus with presence of Alyssum tortuosum (Odontarrhena tortuosa), Cephalaria uralensis, Convolvulus lineatus. Communiies of Elytrigia repens, Calamagrosis epigeios, Festuca regeliana, Galega oicinalis, Puccinellia distans occupy botoms of the valleys. In weter habitats, dominant species are Phragmites australis, Typha angusifolia, Schoenoplectus tabaernaemontani, Bolboschoenus mariimus, Juncus gerardii, Agrosis stolonifera. In the most saline habitats, there are communiies of Limonium alutaceum and Artemisia santonica. Typical lichens of outcrops are Caloplaca aurania, C. saxicolsa, C. variabilis, Candellariella aurella, Lecanora dispersa, Verrucaria nigrescens. Communiies of high shrubs are represented by thickets of Crataegus fallacina, Prunus stepposa. Botanical significance. One of the best steppe areas west to the Dnipro river. 366 Administrative regions. Ternopil region: Berezhany raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 25.0%; F – 10.0%; G – 64.0%; H – 1.0%. 367 Habitats. Level 2. E1 Dry grasslands – 22.0%; E7 Sparsely wooded grasslands – 3.0%; F3 Temperate and mediterranean-montane scrub – 10.0%; G1 Broadleaved deciduous woodland – 12.9%; G3 Coniferous woodland – 52.1%; H5 Miscellaneous inland habitats with very sparse or no vegetation – 1.0%. Futher habitat descripion. E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; F3.2 Submediterranean deciduous thickets and brushes; G3.F Highly artificial coniferous plantations; H5.6 Trampled areas. Land use: forestry (major), mowing/hay making – minor. Protected areas: overlaps (60 ha) with Emerald Site “Berezhanske Opillia”, same as proposed state botanical reserve “Zholoby”. Threats: abandonment/reducion of land management – high, forestry (afforestation) – low. General description. Semi-dry grasslands, plantaions of Pinus sylvestris, natural deciduous woods and shrubs (Prunus spinosa, Crataegus spp.). Grasslands are dominated by Brachypodium pinnatum, Calamagrosis epigeios, Carex humilis. Other frequent species: Centaurea stricta, Filipendula vulgaris, Teucrium chamaedrys. Botanical significance. Large populaion of Orchis militaris. Criterion C • E1.2 Perennial calcareous grassland and basic steppes (6210, *Important orchid site); area: 13 ha; trend: decreasing; area data quality: good; trend data quality: good. Size of populaion of Orchis militaris: 2000–4000 individuals. Conservaion proposals: remove all pine trees, do not allow expansion of trees and shrubs, mow grasslands, non-intensive grazing. Literature 1. Оліяр Г.І., Проців Г.П. Флористичні особливості деяких урочищ Бережанського Опілля // Науковий вісник Національного університету біоресурсів і природокористування України. Серія “Лісівництво та декоративне садівництво” – К.: ВЦ НУБіП України, 2012. – Вип. 171, ч. 1. – С. 131–134. Fraxinus, Acer, Tilia, Ulmus and related woodland; H2.6 Calcareous and ultra-basic screes of warm exposures; H3.2 Basic and ultra-basic inland cliffs. Zhyzhava V.A. Onyshchenko Ukrainian name: Жижава. Area: 107.0 ha. Altitude: 146–300 m. Latitude: 48°41’54” N (48.6983°). Longitude: 25°39’11” E (25.6531°). Administrative regions. Ternopil region: Zalishchyky raion. Ownership: state. Biogeographic regions: coninental. Habitats. Level 1. E – 36.0%; F – 13.0%; G – 40.0%; H – 11.0%. Habitats. Level 2. E1 Dry grasslands – 35.0%; E2 Mesic grasslands – 1.0%; F3 Temperate and mediterranean-montane scrub – 13.0%; G1 Broadleaved deciduous woodland – 40.0%; H2 Screes – 2.0%; H3 Inland clifs, rock pavements and outcrops – 9.0%. Futher habitat descripion. E1.1 Inland sand and rock with open vegetation; E1.2 Perennial calcareous grassland and basic steppes; F3.1 Temperate thickets and scrub; G1.7 Thermophilous deciduous woodland; G1.A Meso- and eutrophic Quercus, Carpinus, 368 Land use: agriculture (animals) – minor, forestry – minor, nature conservation and research – major, tourism/recreaion – minor. Protected areas: overlaps (37 ha) with Zhyzhavskyi state botanical reserve, included in naional nature park “Dnistrovskyi Kanion”, included in Emeral Site “Dnistrovskyi Kanion Naional Nature Park”. Threats: agricultural intensification/expansion (grazing) – low, development (recreaion/ tourism) – low. General description. A steep slope of the Dnister valley with broadleaved forest, steppe vegetaion, shrubs, calcareous rocks and screes. The tree layer of the forest consists of Carpinus betulus, Quercus robur, Quercus petraea, Fraxinus excelsior. The shrub vegetaion is dominated by Prunus spinosa, Staphylea pennata, Crataegus sp. Dominants of the steppe are Carex humilis, Festuca valesiaca, Sipa capillata. There are a lot of protected species: Chamaecyisus podolicus, Iris hungarica, Pulsailla grandis, Pulsailla pratensis, Spiraea 369 polonica etc. Botanical significance. Important for narrow endemic species Spiraea polonica (locus classicus), Podolian steppes, shrubs and rocks with many rare species. Criterion A • Spiraea polonica Błocki; A(iii); abundance: occasional (about 200 individuals in one compact populaion); trend: stable; species data quality: good; trend data quality: medium. Criterion C • E1.11 Euro-Siberian rock debris swards; area: 12 ha; trend: stable; area data quality: poor; trend data quality: good. • F3.247 Ponto-Sarmatic deciduous thickets; area: 14 ha; trend: stable; area data quality: medium; trend data quality: medium. • H2.6 Calcareous and ultra-basic screes of warm exposures; area: 0.5 ha; trend: stable; area data quality: poor; trend data quality: good. Literature 1. Федорончук М.М., Белемець Н.М., Волуца О.Д. Рідкісні види роду Spiraea L. (Rosaceae) флори України та стан їхньої України // Укр. ботан. журн. – 2013. – 70, № 2. – С. 164–167. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. Zolochivka O.T. Kuzyarin, V.A.Onyshchenko Ukrainian name: Золочівка. Area: 398.0 ha. Altitude: 265–280 m. Latitude: 49°46’43” N (49.7786°). Longitude: 24°58’20” E (24.9721°). Administrative regions. Lviv region: Zolochiv raion. Ownership: state (major), private Biogeographic regions: coninental. Habitats. Level 1. C – 0.7%; D – 50.0%; E – 40.3%; F – 1.0%; G – 8.0%. Habitats. Level 2. C1 Surface standing waters – 0.4%; C3 Littoral zone of inland surface waterbodies – 0.3%; D4 Base-rich fens and calcareous spring mires – 30.3%; D5 Sedge and reedbeds, normally without free-standing water – 10.0%; E2 Mesic grasslands – 4.3%; E3 Seasonally wet and wet grasslands – 36.0%; F9 Riverine and fen scrubs – 1.0%; G1 Broadleaved deciduous woodland – 8.0%. Futher habitat descripion. D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; D5.1 Reedbeds normally without free-standing water; D5.2 Beds of large sedges normally without free-standing water; E2.2 Low and medium altitude hay meadows; E3.4 Moist or wet eutrophic and mesotrophic grassland; F9.2 Salix carr and fen scrub. Land use: mowing/hay making – minor. Protected areas: –. Threats: abandonment/reducion of land management – low, agricultural intensiicaion/ 370 expanion (general) – low, water (drainage) – low. General description. Parially drained fen. Major vegetaion types are rich fens and wet grasslands. Dominant species of rich fen are Carex davalliana, Carex lacca, Carex hosiana, Carex panicea, Molinia caerulea, Pragmites australis, Schoenus ferrugineus, Sesleria caerulea, Calliergonella cuspidata, Campylium stellatum, Limprychia revolvens. Other frequent species are Epipacis palustris, Eupatorium cannabinum, Lythrum salicaria, Parnassia palustris, Pinguicula vulgaris, Potenilla erecta, Rinanthus seroinus, Sanguisorba oicinalis, Toieldia calyculata, Valeriana simplicifolia. Meadows are dominated by Briza media, Deschampsia cespitosa, Festuca rubra, Molinia caerulea. Besides there are marshes dominated by Carex acuta and other large sedges without signiicant presence of calciphile species. Botanical significance. One of the largest rich fens in Ukraine with rare species (Sesleria caerulea, Juncus subnodulosus, Dactylorhiza ochroleuca, Dactylorhiza traunsteineri). Criterion C • D4.1 Rich fens, including eutrophic tall-herb fens and calcareous flushes and soaks; area: 140 ha; trend: stable; area data quality: poor; trend data quality: medium. Conservaion proposals. Do not allow recovery of reclamaion ditches, include in Pivnichne Podillia naional nature park and Emerald Site “Pivnichne Podillia”. Literature 1. Кузярін О.Т. Перспективні природоохоронні території басейну верхів’я Західного Бугу // Наукові записки державного природохнавчого музею. – Львів. – 2012. – Вип. 28. – С. 121–130. 2. Червона книга України. Рослинний світ / за ред. Я.П. Дідуха. – К.: Глобалконсалтинг, 2009. – 900 с. 371 Contents Selection criteria ............................................................................................................ 3 Descriptions of IPAs ...................................................................................................... 26 Aiu-Dah (V.A. Onyshchenko) ...................................................................................... 27 Ak-Monaiskyi Step (V.P. Kolomiychuk, V.A. Onyshchenko) ......................................... 29 Arabatska Strilka (V.A. Onyshchenko) ....................................................................... 31 Ardov (R.Ya. Kish) ....................................................................................................... 33 Askania-Nova (V.A. Onyshchenko) .............................................................................. 35 Balakyrivka (V.A. Onyshchenko) ................................................................................. 37 Bereh Syvashyka (V.P. Kolomiychuk, V.A. Onyshchenko) ............................................ 38 Bile Ozero (V.A. Onyshchenko) .................................................................................. 40 Bir na Merli (O.V. Bezrodnova, N.B. Saidakhmedova) ............................................... 42 Bobrovyi Kut (V.P. Kolomiychuk) ................................................................................ 45 Brytavskyi Lis (V.A. Onyshchenko) ............................................................................. 46 Bushchanske Boloto (O.V. Holovko, V.A. Onyshchenko) ............................................ 48 Byriuchyi Ostriv (V.P. Kolomiychuk, V.A. Onyshchenko) ............................................. 50 Cheremske Boloto (V.A. Onyshchenko) ..................................................................... 53 Cherevaskyi Lis (V.A. Onyshchenko) ........................................................................... 55 Chorna Hora (R.Ya. Kish, V.A. Onyshchenko) .............................................................. 56 Chornohora (V.A. Onyshchenko, V.M. Virchenko) ...................................................... 58 Chornyi Lis (V.A. Onyshchenko) ................................................................................. 62 Chortova Hora (V.A. Onyshchenko, N.V. Shumska) .................................................... 64 Chyvchyny (I.I. Chorney, V.A. Onyshchenko) .............................................................. 65 Davydo-Mykilske (V.A. Onyshchenko, M.M. Peregrym) ............................................ 70 Dnipro – Oril (V.A. Onyshchenko) .............................................................................. 72 Dobrianski Hory (V.A. Onyshchenko) ......................................................................... 74 Dolyna Inhulu (V.A. Onyshchenko) ............................................................................ 76 Dolyna Mertvovodu (V.A. Onyshchenko) ................................................................... 78 Dolyna Nartsysiv (V.A. Onyshchenko) ........................................................................ 81 Dubovetski Skhyly (I.M. Danylyk) .............................................................................. 83 Dubrova (R.Ya. Kish, V.A. Onyshchenko) .................................................................... 84 Dunaiski Plavni (V.A. Onyshchenko) ........................................................................... 86 Dzharylhach (V.A. Onyshchenko, V.P. Kolomiychuk) ................................................... 89 Dzhohul (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ................................................... 91 Dziurkach (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ................................................. 93 Gorgany (V.A. Onyshchenko) .................................................................................... 94 Grofa (V.A. Onyshchenko) ......................................................................................... 96 Hadiatski Luky (N.O. Stetsiuk, V.A. Onyshchenko) ..................................................... 98 Halitsynove (V.P. Kolomiychuk) ................................................................................ 101 Holohirskyi Lis (V.A. Onyshchenko) .......................................................................... 103 Homilshanskyi Lis (V.A. Onyshchenko) ..................................................................... 104 Horaivka (L.H. Lubinska, L.T. Horbniak) .................................................................... 106 Horodnytski Tovtry (H.I. Oliiar) ................................................................................ 108 Horodnytskyi Lis (V.A. Onyshchenko) ....................................................................... 110 372 Hostra Skelia (H.I. Oliiar) .......................................................................................... Hrakove (N.O. Stetsiuk) ........................................................................................... Hranitno-Stepove Pobuzhia (V.A. Onyshchenko) ..................................................... Ihrovets – Tavpishyrka (V.A. Onyshchenko, R.Ya. Kish) ............................................. Irpinskyi Lis (V.A. Onyshchenko, O.I. Pryadko) ......................................................... Kadubivska Sinka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) .................................. Kalmiuskyi Step (V.P. Kolomiychuk, V.A. Onyshchenko) ........................................... Kamiani Mohyly (V.A. Onyshchenko, V.P. Kolomiychuk) ........................................... Kanivski Ostrovy (V.A. Onyshchenko) ....................................................................... Kaplivka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak ) ................................................. Karadah (V.A. Onyshchenko) .................................................................................... Karalarskyi Step (V.P. Kolomiychuk, V.A. Onyshchenko) ........................................... Kasova Hora (V.A. Onyshchenko, N.V. Shumska) ...................................................... Kazantyp (V.P. Kolomiychuk, V.A. Onyshchenko) ...................................................... Kedryn (R.Ya. Kish, V.A. Onyshchenko) ..................................................................... Khomutovskyi Step (V.A. Onyshchenko, V.P. Kolomiychuk) ...................................... Kniazhpilskyi Lis (V.A. Onyshchenko) ....................................................................... Kolodiazne (V.A. Onyshchenko, M.V. Banik, O.V. Bezrodnova, V.V. Rasevich) ........... Kolivska Ulohovyna (V.A. Onyshchenko) ................................................................ Koncha-Zaspivskyi Lis (V.A. Onyshchenko) ............................................................... Korsak Mohyla (V.A. Onyshchenko, V.P. Kolomiychuk) ............................................. Kovalivka (Derkach O.M., Kolomiets H.V.) ................................................................ Kozachelaherska Arena (V.A. Onyshchenko) ............................................................ Kreidiana Flora (V.A. Onyshchenko) ......................................................................... Kreidiani Vidslonennia (V.A. Onyshchenko) ............................................................. Kremenchutski Plavni (V.A. Onyshchenko) .............................................................. Krymski Hory (V.A. Onyshchenko) ............................................................................ Kuchuhury (V.P. Kolomiychuk) ................................................................................. Kuchurhan (V.A. Onyshchenko, O.M. Popova) ......................................................... Kurylivka (V.P. Kolomiychuk) .................................................................................... Levkivski Lisy (O.O. Orlov) ........................................................................................ Lysa Hora i Sinka (V.A. Onyshchenko, T.D. Solomakha) ........................................... Lysohirka (V.P. Kolomiychuk) .................................................................................... Marina Hora (V.A. Onyshchenko) ............................................................................. Markovychi (V.V. Datsiuk) ........................................................................................ Marmaroski Hory (V.A. Onyshchenko, V.M. Virchenko) ........................................... Medobory (V.A. Onyshchenko) ................................................................................ Medvezhanka (V.A. Onyshchenko, M.M. Peregrym) ................................................ Mehanom (V.A. Onyshchenko) ................................................................................ Mishkovo-Pohorilove (O.M. Derkach, H.V. Kolomiets) ............................................. Molochnyi Lyman (V.P. Kolomiychuk, V.A. Onyshchenko) ........................................ Morochno-2 (V.A. Onyshchenko) ............................................................................. Mykhailivskyi Step (V.A. Onyshchenko, O.M. Derkach) ............................................ Mykhailo-Laryne (O.M. Derkach, H.V. Kolomiets) .................................................... Mys Martyan (V.A. Onyshchenko) ........................................................................... Mytrofanivskyi Pivostriv (V.P. Kolomiychuk, V.A. Onyshchenko) .............................. Naholnyi Kriazh (V.A. Onyshchenko, M.M. Peregrym) ............................................. Novobila (V.A. Onyshchenko, M.V. Banik) ................................................................ 373 112 114 115 119 121 122 124 126 128 130 132 137 140 142 144 146 148 149 150 152 155 156 158 160 162 164 166 171 173 174 176 178 180 181 182 184 186 190 191 194 196 198 200 202 203 206 208 210 Novohredneve (V.P. Kolomiychuk) ........................................................................... Nyzhnii Dnipro (V.A. Onyshchenko) ......................................................................... Nyzhniodniprovski Pisky (V.A. Onyshchenko) .......................................................... Obytichna Kosa (V.P. Kolomiychuk, V.A. Onyshchenko) ........................................... Olevski Lisy (O.O. Orlov) .......................................................................................... Opuk (V.A. Onyshchenko) ........................................................................................ Oskilski Skhyly (V.A. Onyshchenko, O.V. Bezrodnova, M.V. Banik) ........................... Osovynskyi Step (V.P. Kolomiychuk, V.A. Onyshchenko) .......................................... Pecheniiske Boloto (V.A. Onyshchenko, O.T. Kuzyarin) ............................................ Perebrody (V.A. Onyshchenko, O.I. Pryadko) ........................................................... Peresyp Aktaskoho Ozera (V.P. Kolomiychuk, V.A. Onyshchenko) ............................ Petro-Ivanivka (О.V. Bezrodnova) ............................................................................ Pidlyska Hora (V.A. Onyshchenko, T.D. Solomakha) ................................................. Podvirivka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) .............................................. Pohorylivka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ............................................ Polonskyi Lis (V.A. Onyshchenko) ............................................................................. Polonyna Borzhava (V.A. Onyshchenko) .................................................................. Polovetskyi Step (V.P. Kolomiychuk) ........................................................................ Potashnianski Lisy (O.O. Orlov, V.A. Onyshchenko) .................................................. Probabyn (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ............................................... Provalskyi Step (V.A. Onyshchenko) ......................................................................... Riznykivka (V.A. Onyshchenko) ................................................................................ Romosh (V.V. Datsiuk, V.A. Onyshchenko) ............................................................... Rys (V.A. Onyshchenko) ........................................................................................... Samarskyi Lis (V.A. Onyshchenko) ............................................................................ Savranskyi Lis (V.A. Onyshchenko) ........................................................................... Serbyno (V.A. Onyshchenko) .................................................................................... Sharivka (V.A. Onyshchenko, M.V. Banik) ................................................................. Shatski Ozera (V.A. Onyshchenko) ........................................................................... Shebutynskyi Yar (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) .................................... Sinozhai (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ................................................ Skhidne Roztochia (V.A. Onyshchenko) .................................................................... Skhidnyi Churiuk (V.P. Kolomiychuk,V.A. Onyshchenko) ........................................... Skhyly Kohylnyka (V.A. Onyshchenko, O.M. Popova) ............................................... Skhyly Krasnoi i Kobylky (V.A. Onyshchenko) ........................................................... Slovechanskyi Kriazh (V.A. Onyshchenko) ................................................................ Somyno (V.A. Onyshchenko) .................................................................................... Sovyi Yar (V.A. Onyshchenko) ................................................................................... Striltsivskyi Step (V.A. Onyshchenko) ....................................................................... Stuzhytsia (V.A. Onyshchenko) ................................................................................ Sviai Hory (V.A. Onyshchenko) ................................................................................ Svydovets (V.A. Onyshchenko) ................................................................................. Syra Pohonia (V.A. Onyshchenko) ............................................................................ Tarkhankut (V.A. Onyshchenko) ............................................................................... Tendrivska Zatoka (V.A. Onyshchenko, O.Yu. Umanets) ........................................... Tepe-Oba (V.A. Onyshchenko) ................................................................................. Ternava – Dnister (V.A. Onyshchenko) ..................................................................... Tiup-Tarkhan i Kalynivskyi Pivostriv (V.P. Kolomiychuk, V.A. Onyshchenko) ............. 374 212 213 215 218 220 221 224 227 229 230 232 234 236 238 239 241 243 244 246 248 249 252 253 255 256 259 260 261 262 266 267 269 271 273 274 276 277 279 280 284 286 289 293 294 298 300 303 306 Tovtrivska Sinka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) .................................... 307 Triokhizbenskyi Step (V.A. Onyshchenko) ................................................................ 309 Troitska Balka (V.P. Kolomiychuk, V.A. Onyshchenko) .............................................. 311 Trosianets (V.A. Onyshchenko, O.M. Popova) ......................................................... 312 Tsetsyno (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ................................................. 314 Tulyntsi – Makedony (V.A. Onyshchenko) ................................................................ 315 Turova Dacha (V.A. Onyshchenko, N.V. Shumska) .................................................... 317 Ubort – Bolotnytsia (V.A. Onyshchenko) .................................................................. 318 Uholka – Shyrokyi Luh (V.A. Onyshchenko) .............................................................. 321 Usia – Shutnivtsi (L.H. Lubinska, V.A. Kolodiy) ........................................................ 323 Vasylivka (V.P. Kolomiychuk, L.V. Markivska) ............................................................ 325 Vasylivskyi i Rozkopynskyi Yary (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ............... 326 Velyki Holdy (N.V. Shumska, V.A. Onyshchenko) ...................................................... 328 Verbetska Tovtra (V.A. Onyshchenko) ....................................................................... 330 Verkhniobuzki Lisy (V.A. Onyshchenko) .................................................................... 331 Vitrohon (V.A. Onyshchenko) .................................................................................... 333 Volyzhyn Lis (V.A. Onyshchenko, O.Yu. Umanets) .................................................... 334 Vovchanski Skhyly (V.A. Onyshchenko, O.V. Bezrodnova, M.V. Banik) ..................... 336 Vtenske Boloto (V.A. Onyshchenko) ........................................................................ 338 Vymushiv (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ............................................... 339 Vyshnivka (I.I. Chorney, A.I. Tokaryuk, V.V. Budzhak) ............................................... 341 Yaiko Perehinske (V.A. Onyshchenko) ...................................................................... 342 Yelanetskyi Step (V.A. Onyshchenko) ....................................................................... 343 Yemilchynski Lisy (O.O. Orlov, V.A. Onyshchenko) ................................................... 346 Yulivski Hory (R.Ya. Kish, V.A. Onyshchenko) ............................................................ 348 Zaplava Desny (V.A. Onyshchenko, O.V. Lukash) ...................................................... 349 Zaplava Latorytsi (V.A. Onyshchenko) ...................................................................... 353 Zaplava Prypiai (V.A. Onyshchenko) ....................................................................... 355 Zaplava Siverskoho Dintsia (V.A. Onyshchenko) ....................................................... 357 Zaplava Tysy (R.Ya. Kish, V.A. Onyshchenko) ............................................................. 359 Zaplavni Lisy na Borzhavi (R.Ya. Kish, V.A. Onyshchenko) ........................................ 361 Zaplavy Dnipra i Sozha (V.A. Onyshchenko, O.V. Lukash) ......................................... 362 Zelena Balka (V.A. Onyshchenko) ............................................................................. 365 Zholoby (H.I. Oliiar, H.P. Protsiv) .............................................................................. 367 Zhyzhava (V.A. Onyshchenko) .................................................................................. 368 Zolochivka (O.T. Kuzyarin, V.A. Onyshchenko) .......................................................... 370 375 Наукове видання Важливі ботанічні території України За редакцією д.б.н. В.А. Онищенка Підписано до друку 16.05.2017. Формат: 60 x 84/16. Папір офс. Гарнітура: Calibri. Друк офс. Умов. друк. арк. 21,86 Замовлення № 2017-10 “Альтерпрес”, 01034 Київ, вул. В. Житомирська, 28. Свідоцтво про реєстрацію ДК №177 від 15.09.2000 р. Віддруковано: “Альтерпрес”, 04112 Київ, вул. Шамрила, 23 376