Achillea asplenifolia Vent. is one of three central European diploid species (together with A. setacea Waldst. et Kit. and A. roseoalba Ehrend.) of the A. millefolium group. Its taxonomic and phytogeographic account from the central European perspective is given mainly on the basis of herbarium and field studies. The synonymy of A. asplenifolia includes A. millefolium var. crustata Rochel and A. scabra Host; both names are typified here. No variation deserving taxonomic recognition was observed. From the taxonomic point of view, A. asplenifolia is a clearly delimited species. It grows in the Czech Republic, Slovakia, Austria, Hungary, Croatia, Serbia, and Romania. From the phytogeographic point of view, it can be classified as a Pannonian geoelement with overlaps to Transylvania and to the marginal parts of the eastern Mediterranean. Within the Czech Republic, its distribution range includes only the warmest and driest part of southern Moravia, with the northernmost site situated near the town of Vyškov. In southern Moravia, A. asplenifolia was confined to extrazonal habitats, mainly to islands of halophilous vegetation such as moist saline meadows (formerly used as pastures) and lowland fens rich in mineral nutrients, but most of the sites were destroyed. Out of six or seven localities preserved up to present, only two host vital populations.
Comments on 11 species of cyanophilic lichens are presented. A new combination Peccania cernohorskyi is proposed, commented on and typified. Anema nodulosum, A. prodigulum, Lempholemma intricatum, Leptogium ferax, Porocyphus rehmicus and Zahlbrucknerella calcarea are reported from Slovakia for the first time, Leptogium biatorinum and L. magnussonii from Hungary, and Anema prodigulum, Heppia adglutinata, Leptogium biatorinum and Psorotichia taurica from the Czech Republic. Leptogium cretaceum is lectotypified.
The occurrence in the Mediterranean part of Europe of the African species Potamogeton schweinfurthii is recorded for the first time. So far, this native but overlooked species has been found on five major Mediterranean islands: Corsica, Sardinia, Malta, Kefallinía (Ionian Islands, Greece) and Crete. The species is most similar and presumably closely related to the mainly Eurasian P. lucens, with which it has been partly confused. The nomenclature and a description of P. schweinfurthii are provided, and its taxonomy and how it differs from similar taxa discussed. All known localities are listed, together with voucher specimens preserved in the major European herbaria. A distribution map of P. schweinfurthii in the Mediterranean region is presented.
A new bramble species, Rubus silvae-norticae, section Rubus, subsection Hiemales E. H. L. Krause in Prahl, series Micantes Sudre, which occurs in S Bohemia, Upper Austria and Lower Bavaria, is described. It is recorded at 130 localities. The distance between the most remote localities is ca 100 km. The species grows most frequently in forest habitats (as a distinctly nemophilous ecoelement) such as ditches and edges of forest roads, plantations, forest margins and clearings. It mainly grows in mesic, acid and mineral-poor soils. Like, for example, R. clusii or R. ser. Glandulosi and unlike other relatively thermophilous Rubus species, it is able to grow and propagate itself at rather high altitudes, up to the mountain vegetation belt. The diagnostic characters that separate R. silvae-norticae from its most similar and sympatrically occurring species, R. clusii and R. muhelicus, are provided. In Austria R. silvae-norticae and some other brambles were mistakenly considered as R. helveticus, a bramble (probably a single biotype) described from Switzerland in 1870. The lectotype of Rubus helveticus is designated here and a photograph of the specimen presented. Also included is a distribution map of R. silvae-norticae, a list of revised herbarium specimens, a photograph of the type specimen and a pen drawing of the species. The significance of regional brambles for plant migrations and phytogeography is shown, based on the distribution of selected regional Rubus species occurring in the Czech and Austrian border area, which is a known mountain barrier to migration. The distribution patterns of the brambles support a theory about the routes of plant migration and the florogenetic connection between Austria and the Czech Republic. Rubus silvae-norticae, R. muhelicus and R. vestitus f. albiflorus are regarded as Danubian migrants (distributed from Upper Austria to S Bohemia), whereas R. gothicus s. l. (“south Moravian type”) and R. austromoravicus are considered to be Dyje-Kamp migrants (distributed from Moravia and Lower Austria to S Bohemia) within the Bohemian flora. Rubus kletensis is supposed to be a Vltava migrant within the Austrian flora (distributed from S Bohemia to Upper Austria).
Specimens of Viola elatior (VE), V. pumila (VP) and V. stagnina (VS) in 40 Austrian, Czech and Slovak public herbaria were revised, a total of almost 1750 specimens from the three countries. Apart from VE, the quality of the original identifications was rather poor, especially of VS, which was frequently confused with VP and V. canina. This, together with the confusion of nomenclature that persisted during the 19th century, made the old literature records unreliable. Hybrids are usually difficult to identify and are rarer than generally believed. VS and VP have similar distribution patterns: they occur mainly on floodplains of large lowland rivers and in adjacent hills in the N part of Bohemia, S and Central Moravia, E Austria and S Slovakia; they may be classified as river corridor plants. VS differs from VE and VP mainly by its presence in S Bohemia and its absence from large parts of S Slovakia, as well as its rarity in Austria and Slovakia. All three species grow predominantly in regions with a relatively warm and dry climate: most localities are situated in regions with a mean annual temperature of 7–11 °C and mean annual precipitation 401–700 mm. A temporal analysis of records revealed that all three species are declining in all three countries: generally, this decline is weakest in Austria, with 46–61% of grid cells with occurrences confirmed after 1980 (compared with the number of grid cells with records for 1801–2008), and strongest in Slovakia, with 18–32% of grid cells with occurrences confirmed after 1980. The decline is due mainly to the canalization of rivers and subsequent changes in land use, urbanization and recently afforestation. VE may also be endangered by modern forestry practices. The inclusion of all three species in national Red Lists and subsequent conservation measures are justified and necessary, though national Red List status may differ between countries.