Rare and Threatened plants of the island of Pag

Rijetka i ugrožena vaskularna flora otoka Paga analizirana je s obzirom na primjenu kategorija ugroženosti iz 1994. i 2005. godine. S obzirom na katego-rizaciju ugroženosti iz 2005. godine, za otok Pag zabilježene su 33 vrste i pod-vrste ugroženih biljaka. Od 33 svojte (vrste i podvrste), osam je kritično ugrože-no (CR), sedam je ugroženo (EN), a 18 svojti pripada kategoriji osjetljivih (VU).Rare and threatened vascular plants of the island of Pag were analysed according to 1994 and 2005 Red Books. Based on 2005 Red Book, the flora of the island of Pag includes 33 treatened taxa (species and subspecies). Eight of them are critically endangered (CR), seven are in the endangered category (EN) and 18 taxa belong to the vulnerable category (VU)

Taxonomic Composition of Pasture Flora on Ćićarija (Istria, Croatia)

Autochthonous vascular pasture fl ora was researched at the localities of two family owned farms which breed sheep, situated on the Ćićarija mountain (Istria, Croatia). During research conducted in 2003 and 2004, a total of 314 plant taxa (279 species, 34 subspecies and 1 variety) were found. The taxa belonged to 173 genera and 45 families. Th e most dominant families are: Asteraceae with 49 species and 2 subspecies, and Poaceae with 34 species and 4 subspecies, followed by Lamiaceae with 26 species and 6 subspecies, and Fabaceae with 22 species and 6 subspecies. According to analysis of life forms, the most numerous are hemicryptophytes (53.82%) and therophytes (22.93%). Phytogeographical analysis has shown that the most pasture plants belong to the Mediterranean fl oral element (32.91%) and Euro-Asiatic floral element (29.17%)

Taxonomic Composition of Pasture Flora on Ćićarija (Istria, Croatia)

Autochthonous vascular pasture fl ora was researched at the localities of two family owned farms which breed sheep, situated on the Ćićarija mountain (Istria, Croatia). During research conducted in 2003 and 2004, a total of 314 plant taxa (279 species, 34 subspecies and 1 variety) were found. The taxa belonged to 173 genera and 45 families. Th e most dominant families are: Asteraceae with 49 species and 2 subspecies, and Poaceae with 34 species and 4 subspecies, followed by Lamiaceae with 26 species and 6 subspecies, and Fabaceae with 22 species and 6 subspecies. According to analysis of life forms, the most numerous are hemicryptophytes (53.82%) and therophytes (22.93%). Phytogeographical analysis has shown that the most pasture plants belong to the Mediterranean fl oral element (32.91%) and Euro-Asiatic floral element (29.17%)

Floristic characteristics of rotational grazing pastures near Puntera (Istria, Croatia

Samonikla vaskularna flora pašnjaka istraživana je na lokalitetima obi-teljskog gospodarstva s ovčarskom proizvodnjom u Punteri u Istri. Tijekom istraživanja 2004. i 2005. godine ustanovljeno je 100 biljaka (91 vrsta i 9 podvrsta) iz 80 rodova i 24 porodice. Većina biljaka pripada porodicama Gramineae (19%), Compositae (16%) i Leguminosae (16%). U spektru ži-votnih oblika prevladavaju hemikriptofiti (52%) i terofiti (36%).Autochthonous vascular pasture flora was researched at the locality of a family owned farm breeding sheep, situated near Puntera in Istria, Croatia. During the research in 2004 and 2005, a total of 100 plant taxa (91 species and 9 subspecies) were found. The taxa belonged to 80 genera and 24 families. The most dominant families were: Gramineae (19%), Compositae (16%) and Leguminosae (16%). According to the analysis of life forms, the most numerous were Hemicryptophyta (52%) and Therophyta (36%)

MEDICINAL AND AROMATIC PLANTS OF ROCKY PASTURES ON THE NORTHERN ADRIATIC ISLANDS

Tijekom istraživanja samonikle vaskularne flore kamenjarskih pašnjaka sjevernojadranskih otoka Krka, Cresa i Paga utvrđeno je 59 ljekovitih i aromatičnih biljaka. Od ustanovljenih 59 vrsta, prema načinu korištenja, najviše vrsta − njih 43 − može se koristiti u ljekovite svrhe, aromatičnih biljaka ima 4 vrste, dok 12 vrsta istovremeno pripada u ljekovite i aromatične biljke. Analizom ekoloških indikatorskih vrijednosti utvrđeno je da su istraživane ljekovite i aromatične biljke većinom prilagođene uvjetima umjereno toplih i suhih staništa izloženih suncu. S obzirom na indikatorske vrijednosti za reakciju tla (pH), proučavane vrste imaju vrlo različite vrijednosti, odnosno podjednako su zastupljene vrste koje mogu rasti na kiselim, kao i one koje mogu rasti na alkaličnim tlima. Među istraživanim ljekovitim i aromatičnim biljkama, najzastupljenije su vrste koje su prilagođene tlima siromašnim hranjivima.In the study of the wild vascular flora growing in rocky pastures of the northern Adriatic islands of Krk, Cres and Pag, 59 medicinal and aromatic plants were found. According to their use, most species - 43 - out of 59 found, can be used for medicinal purposes, 4 species belong to aromatic plants, while 12 species belong to both medicinal and aromatic plants. The analysis of ecological indicator values found that the studied medicinal and aromatic plants were mostly adapted to the conditions of moderately hot and dry habitats exposed to the sun. Given the indicative values for the soil reaction (pH), the studied species have very different values, that is, species that can grow in acidic soil and those that can grow in alkaline soil are equally represented. Among the studied medicinal and aromatic plants, the most common species are those that are adapted to soils that are poor in nutrients

Nova nalazišta Sisyrinchium bermudiana L. (Iridaceae) u Hrvatskoj

New, as well as already known localities of the Sisyrinchium bermudiana species in Croatia, are listed in the paper. The new localities are situated in Gornja Stubica (Hrvatsko Zagorje) and Rakov Potok, to the east of Samobor. The species grows in the scope of meadow and grass vegetation in these localities.Navode se nova, kao i dosad poznata nalazišta vrste Sisyrinchium bermudiana u Hrvatskoj. Nova su nalazišta Gornja Stubica u Hrvatskom Zagorju i Rakov Potok istočno od Samobora. Na tim lokalitetima navedena vrsta raste u sastavu livadne i travnjačke vegetacije

FLORISTIC AND VEGETATION CHARACTERISTIC OF FOREST EDGES AND GRASSLANDS OF ĆIĆARIJA (CROATIA)

Cilj ovog istraživanja bio je utvrditi floru i vegetaciju travnjaka, te prisutnost i učestalost pojavljivanja drvenastih i zeljastih svojti šumskog ruba na lokalitetima s različitim načinom gospodarenja (livade/pašnjaci; korišteno/nekorišteno). Istraživanja flore i vegetacije travnjaka (2008–2010) provedena su na 27 lokaliteta. Pritom su napravljene 103 fitocenološke snimke po Braun-Blanquetovoj metodi. Travnjaci Ćićarije većinom pripadaju redu Scorzonero-Chrysopogonetalia (pašnjaci) te manjim dijelom redu Arrhenatheretalia (livade). Na istraživanim travnjacima Ćićarije zabilježene su ukupno 624 biljne svojte, razvrstane u 275 rodova i 62 porodice; najzastupljenije su biljke mediteranskog flornog elementa (31,15 %) i euroazijskog flornog elementa (29,97 %). Od životnih oblika prevladavaju hemikriptofiti (53,83 %). Od ukupne flore izdvojeno je 35 drvenastih svojti (5,61 % ukupne flore) i 74 zeljaste svojte šumskog ruba (11,86 % ukupne flore) iz razreda Trifolio-Geranietea sanguinei, koje ukazuju na započete procese vegetacijske sukcesije na pojedinim lokalitetima. Među zeljastim vrstama na većini je lokaliteta zabilježeno zarastanje s Brachypodium rupestre. Osobitu pozornost treba posvetiti zaštiti i očuvanju istraživanih travnjaka kroz mjere gospodarenja (ispaša i košnja), sprječavanja započetog procesa sukcesije travnjaka i održanja kontrole širenja kolonizatorske vrste B. rupestre. Rezultati istraživanja mogu pružiti osnovu za izradu planova upravljanja te očuvanja bioraznolikosti, posebice na područjima unutar mreže Natura 2000.The aim of this study was to determine grassland flora (Tab. 2) and vegetation, and frequency of occurrence of woody and herbaceous species of the forest edge at different grassland management localities (Tab. 6, see Tab. 5). The field research of flora and grassland vegetation (2008–2010) was conducted at 27 localities (Tab. 1, Fig.1). A total of 103 relevés using the Braun-Blanquet (1964) method amounting to 100 m2 was made, while the description of habitats included geographical coordinates, altitude, inclination, exposure, land forms, and grassland management. Woody species and herbaceous transgressive species from the Trifolio-Geranietea sanguinea class (according to Kaligarič 1997) were selected from the relevés (Vitasović Kosić 2011) and are hereinafter referred to as "herbaceous species of the forest edge". The presence and frequency of each taxon in relation to the type of grassland management were determined. For each taxon, Braun-Blanquet’s values were calculated as percentage of ground cover (%) on a particular grassland type and classified according to grassland management type. From a total of 103 relevés, 35 relevés were abandoned pastures (NP), 23 relevés abandoned meadows (NL), 20 relevés used pastures (KP) and 25 relevés used meadows (KL). The diversity of environmental grassland parameters and grassland management type was determined using modified Ellenberg indicator values (EIV) adjusted for the Mediterranean (Pignatti et al. 2005). The descriptive statistical analysis of environmental variables (Box & Whiskers diagrams) was conducted using the STATISTICA software package (StatSoft Inc. 2005). A total of 624 plant taxa classified in 275 genera and 62 families was recorded whereas the top six families according to number of taxa (Asteraceae, Fabaceae, Poaceae, Lamiaceae, Liliaceae and Rosaceae) encompassed more than half (51.28 %) of the total recorded flora (Tab. 3). According to phytogeographical analysis (Tab. 4), the nearly equal representation of the Mediterranean floral element (31.15 %) and Eurasian floral element (29.97 %) indicated that the studied area is located at the transition between the sub-Mediterranean and Mediterranean-mountain vegetation belt. Prevalent life forms include hemicryptophytes (53.83 %), which are typical for the grassland flora of pastures and meadows and indicate anthropogenic influence reflected in the form of grazing and burning. The relatively high prevalence of woody plants in the grassland habitats (N and P, 5.59 %) indicated processes of succession at some of the localities (Fig. 2). The Ćićarija grasslands belong mostly to the Scorzonero-Chrysopogonetalia order (pastures) and partially to the Arrhenatheretalia order (meadows) (Poldini 1989, Kaligarič 1997, Poldini & Kaligarič 1997, Vitasović Kosić et al. 2011, 2012). A syntaxonomical interpretation of these associations is shown below. From the total flora, 35 woody species (5.61 %) and 74 herbaceous species of the forest edge (11.86 %) from the class Trifolio-Geranietea sanguinei were singled out, indicating processes of vegetation succession at some of the localities (Tab. 5, Tab. 6). Among the endangered species, Gentiana symphyandra (EN) and the vulnerable Lilium bulbiferum (VU) should be noted. According to grassland management, the largest number of woody and herbaceous species of the forest edge was detected within abandoned areas: NP – 58 taxa and NL – 28 species, while the used areas KL (16 taxa) and KP (7 species) contained significantly less. The analysis of ecological indicator values (EIV) for woody and herbaceous species of forest edges (Fig. 3) showed that KP distinguished among the grassland management types, as can be seen by EIV nutrients, continentality, and light. Used pastures are generally homes to species that grow in poor soil nutrients (e.g., Genista sylvestris and Inula hirta), subcontinental (e.g., Asparagus tenuifolius), and continental species (e.g., Chamaecytisus hirsutus). As for the EIV of light, used pastures have more half-shade species, some of which cannot grow under full light (e.g., Helleborus multifidus subsp. istriacus). Contrary are used meadows where generally full-light species appear (Orobanche minor, Scabiosa columbaria, Rhinanthus aristatatus, etc.). It is known that grassland management acts as a driving force in the diversity of the plant community (MacDonald et al. 2000, Kahmen et al. 2002, Wilson et al. 2003). During the last six decades, the abandonment of the traditional way of raising sheep resulted in different succession changes and significantly influenced biodiversity (Zupančić and Žagar 2002, de Bello et al. 2007). The main overgrowth of vegetation occurred in the contact zones between inadequately mowed and grazing plots. Other means of spreading woody species may include forest edges and shrub communities that occur as a phase in the very dynamic process of re-overgrowth, which most often has an anthropogenic origin (Čarni et al. 2002). Immediately after a plot ceases to be mowed or used for grazing, the occurrence of a high percentage of successional species is almost instant (Poldini 1989, Kaligarič & Poldini 1997, see Tab. 6). Due to the low usage intensity of grasslands, the colonizing grass Brachypodium rupestre spread across the entire plot (Catorci et al., 2011, 2012). In this study B. rupestre appeared at a large frequency (<40 %) on KL and KP, and with an even greater frequency (>40 %) on NL and NP (see Tab. 5, compare Vitasović Kosić et al. 2012). The occurrence of B. rupestre in Ćićarija is consistent with several studies, all of which emphasize the role of B. pinnatum and B. rupestre in the invasion of unmanaged grasslands through processes of competition and related problems of conservation (During & Willems 1984, Bobbink & Willems 1987). According to Grime (1973, 2001), B. rupestre possesses dominant features such as large size, strong vegetative reproductive capacity (with marked lateral spreading), growth from basal meristems (Stebbins 1972), and high phytomass production (Catorci et al. 2012). Moreover, its silica-rich leaves render this species poorly palatable for sheep (Grime et al. 1988), thus enabling the formation of a large amount of plant litter and a consequent decrease in floristic diversity (Bonanomi and Allegrezza 2004; Bonanomi et al. 2009). Under-grazing and irregular mowing (i.e., low disturbance) lead to the floristic homogenization of a system (Vitasović Kosić et al. 2011), which ultimately leads to a reduction in plant diversity. Meadows are subjected to the invasion of B. rupestre to a larger extent and, as stated by Bennie et al. (2006), they are more vulnerable to the loss of floristic diversity than pastures after regular management ceases. For this reason, regular mowing should be maintained and intensified. As for dry pastures, a solution for more efficient management could be in using very low selective herbivores, such as cows, donkeys or horses, for grazing. In conclusion, particular attention in the protection and preservation of grasslands should be given to certain management measures (grazing and mowing) in order to maintain biodiversity, prevent grassland succession, and maintain control of the spread of B. rupestre. The results of this research can provide the basis for the development of new management plans, which will require specific knowledge on the preservation of biodiversity, particularly in Special Protected Areas (SPA) within the Natura 2000 network. Syntaxonomical interpretation: FESTUCO-BROMETEA Braun-Blanquet et R. Tüxen 1943 SCORZONERO-CHRYSOPOGONETALIA Horvatić et Horvat (1956) 1958 Saturejon subspicatae Horvatić 1975    Carici humili-Centaureetum rupestris Horvat 1931    aa) subas. satureetosum variegatae Poldini 1989 (= as. Saturejo subspicatae-Caricetum humilis Trinajstić /1981/1999, corr.2007)    ab) subas. laserpitietosum sileris Kaligarič et Poldini 1997, variant with Laserpitium siler (so far observed only in Gorski Kotar)    ac) subas. seslerietosum juncifoliae Horvat 1962 (= as. Seslerio juncifoliae-Caricetum humilis Horvat 1930) Scorzonerion villosae Horvatić 1949       Danthonio-Scorzoneretum villosae Horvatić (1956) 1958          subas. koelerietosum macranthae Vitasović Kosić 2011.       Bromo-Chrysopogonetum grylli Horvat 1960 BROMETALIA ERECTI Braun-Blaunquet 1936       Bromion erecti W. Koch 1926           Koelerio pyramidatae-Brachypodietum rupestris Trinajstić (1981) 2005 MOLINIO-ARRHENATHERETEA R. Tüxen 1937 ARRHENATHERETALIA Pawlowski 1928       Arrhenaterion elatioris Braun-Blaunquet 1926          subas. Anthoxantho-Brometum erecti Poldini 1980 (= subas. Arrhenatheretum elatioris brometosum erecti Poldini 1989) – first time recorded in Croati