36 research outputs found
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 kritiÄno 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 ÄiÄarija (Istria, Croatia)
Autochthonous vascular pasture fl ora was researched at the localities of two family owned farms which breed sheep, situated on the ÄiÄarija 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 paÅ”njaka istraživana je na lokalitetima obi-teljskog gospodarstva s ovÄarskom 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. VeÄina 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%)
Nova nalaziŔta 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 nalaziÅ”ta vrste Sisyrinchium bermudiana u Hrvatskoj. Nova su nalaziÅ”ta Gornja Stubica u Hrvatskom Zagorju i Rakov Potok istoÄno od Samobora. Na tim lokalitetima navedena vrsta raste u sastavu livadne i travnjaÄke vegetacije
MEDICINAL AND AROMATIC PLANTS OF ROCKY PASTURES ON THE NORTHERN ADRIATIC ISLANDS
Tijekom istraživanja samonikle vaskularne flore kamenjarskih paÅ”njaka sjevernojadranskih otoka Krka, Cresa i Paga utvrÄeno je 59 ljekovitih i aromatiÄnih biljaka. Od ustanovljenih 59 vrsta, prema naÄinu koriÅ”tenja, najviÅ”e vrsta ā njih 43 ā može se koristiti u ljekovite svrhe, aromatiÄnih biljaka ima 4 vrste, dok 12 vrsta istovremeno pripada u ljekovite i aromatiÄne biljke. Analizom ekoloÅ”kih indikatorskih vrijednosti utvrÄeno je da su istraživane ljekovite i aromatiÄne biljke veÄinom prilagoÄene uvjetima umjereno toplih i suhih staniÅ”ta izloženih suncu. S obzirom na indikatorske vrijednosti za reakciju tla (pH), prouÄavane vrste imaju vrlo razliÄite vrijednosti, odnosno podjednako su zastupljene vrste koje mogu rasti na kiselim, kao i one koje mogu rasti na alkaliÄnim tlima. MeÄu istraživanim ljekovitim i aromatiÄnim biljkama, najzastupljenije su vrste koje su prilagoÄene tlima siromaÅ”nim 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
FLORISTIC AND VEGETATION CHARACTERISTIC OF FOREST EDGES AND GRASSLANDS OF ÄIÄARIJA (CROATIA)
Cilj ovog istraživanja bio je utvrditi floru i vegetaciju travnjaka, te prisutnost i uÄestalost pojavljivanja drvenastih i zeljastih svojti Å”umskog ruba na lokalitetima s razliÄitim naÄinom gospodarenja (livade/paÅ”njaci; koriÅ”teno/nekoriÅ”teno). Istraživanja flore i vegetacije travnjaka (2008ā2010) provedena su na 27 lokaliteta. Pritom su napravljene 103 fitocenoloÅ”ke snimke po Braun-Blanquetovoj metodi. Travnjaci ÄiÄarije veÄinom pripadaju redu Scorzonero-Chrysopogonetalia (paÅ”njaci) te manjim dijelom redu Arrhenatheretalia (livade). Na istraživanim travnjacima ÄiÄarije 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 Å”umskog ruba (11,86 % ukupne flore) iz razreda Trifolio-Geranietea sanguinei, koje ukazuju na zapoÄete procese vegetacijske sukcesije na pojedinim lokalitetima. MeÄu zeljastim vrstama na veÄini je lokaliteta zabilježeno zarastanje s Brachypodium rupestre.
Osobitu pozornost treba posvetiti zaÅ”titi i oÄuvanju istraživanih travnjaka kroz mjere gospodarenja (ispaÅ”a i koÅ”nja), sprjeÄavanja zapoÄetog procesa sukcesije travnjaka i održanja kontrole Å”irenja kolonizatorske vrste B. rupestre. Rezultati istraživanja mogu pružiti osnovu za izradu planova upravljanja te oÄuvanja bioraznolikosti, posebice na podruÄjima 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 (2008ā2010) was conducted at 27 localities (Tab. 1, Fig.1). A total of 103 relevĆ©s 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 KaligariÄ 1997) were selected from the relevĆ©s (VitasoviÄ KosiÄ 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-Blanquetās 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 relevĆ©s, 35 relevĆ©s were abandoned pastures (NP), 23 relevĆ©s abandoned meadows (NL), 20 relevĆ©s used pastures (KP) and 25 relevĆ©s 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 ÄiÄarija grasslands belong mostly to the Scorzonero-Chrysopogonetalia order (pastures) and partially to the Arrhenatheretalia order (meadows) (Poldini 1989, KaligariÄ 1997, Poldini & KaligariÄ 1997, VitasoviÄ KosiÄ 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 ā 58 taxa and NL ā 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 (ZupanÄiÄ 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 (Äarni 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, KaligariÄ & 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 VitasoviÄ KosiÄ et al. 2012). The occurrence of B. rupestre in ÄiÄarija 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 (VitasoviÄ KosiÄ 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. TĆ¼xen 1943
SCORZONERO-CHRYSOPOGONETALIA HorvatiÄ et Horvat (1956) 1958
Saturejon subspicatae HorvatiÄ 1975
Carici humili-Centaureetum rupestris Horvat 1931
aa) subas. satureetosum variegatae Poldini 1989 (= as. Saturejo subspicatae-Caricetum humilis TrinajstiÄ /1981/1999, corr.2007)
ab) subas. laserpitietosum sileris KaligariÄ 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 HorvatiÄ 1949
Danthonio-Scorzoneretum villosae HorvatiÄ (1956) 1958
subas. koelerietosum macranthae VitasoviÄ KosiÄ 2011.
Bromo-Chrysopogonetum grylli Horvat 1960
BROMETALIA ERECTI Braun-Blaunquet 1936
Bromion erecti W. Koch 1926
Koelerio pyramidatae-Brachypodietum rupestris TrinajstiÄ (1981) 2005
MOLINIO-ARRHENATHERETEA R. TĆ¼xen 1937
ARRHENATHERETALIA Pawlowski 1928
Arrhenaterion elatioris Braun-Blaunquet 1926
subas. Anthoxantho-Brometum erecti Poldini 1980 (= subas. Arrhenatheretum elatioris brometosum erecti Poldini 1989) ā first time recorded in Croati