The investigation of three streams in the Moravian part of the Javorníky Mts in 2003 and 2006–2009 brings the first records of Plecoptera in these mountains. A total of 28 species and were found (30 % of the recent fauna of the Czech Republic), among which species of the upper parts of streams predominate. This result corresponds to the nature of the habitat on which researches have been carried out. One endangered species (Leuctra cf. major), two vulnerable species (Dinocras cephalotes, Perla marginata) and one near threatened species (Leuctra quadrimaculata) were recorded. Comparing the recorded species to those of the neighbouring mountains, it can be assumed that the fauna of stoneflies of the Javorníky Mts may contain more than 40 species and can form a continuous transition between the Moravskoslezské Beskydy Mts and the Bílé Karpaty Mts (including the Vizovická vrchovina Highlands).
Collections of benthic organisms were obtained during previous Soviet research cruises in the Mediterranean Sea, 1974–1980. Material was collected by bottom grabs or trawls from the depths of 20-500m. Collecting stations were allocated in the Aegean, Adriatic, Tyrrhenian, Balearic, Alboran, and Ionian Seas, and between Sicily and Tunisia. Among decapod crustaceans collected, 8 species of portunid crabs were present, i.e., Liocarcinus. corrugatus (Pennant, 1777), L. depurator (Linnaeus, 1758), L. maculatus (Risso, 1827), L. navigator (Herbst, 1794), L. vernalis (Pennant, 1816), L. zariquieyi Gordon, 1968, Macropipus tuberculatus (Roux, 1830), and Bathynectes longipes (Risso, 1816). For two species, L. maculatus and L. zariquieyi, new distributional records are presented here. An extension of the known depth range is reported here for L. maculatus and L. vernalis.
The paper reports on finds of the invasive species Senecio inaequidens along motorways in Poland and Slovakia. The species was already mentioned in the floras of both countries but until recently there had been no reports from motorways there. In 2015, a large population of Senecio inaequidens was found along the A4 motorway in Poland. In 2013, it was collected along the D2 motorway in Slovakia. Intensive road traffic is probably the main vector of Senecio inaequidens invasion along motorways in Central Europe. Motor vehicles can carry the propagules over long distances. The newly recorded sites along the A4 in Poland and the D2 in Slovakia are part of the species’ invasion eastwards. It is assumed that Senecio inaequidens will continue to spread along motorways in both countries and in the region as a whole.
The paper presents information about habitat conditions of occurrence of the Ptychoverpa bohemica (Krombh.) Boud. fungus in man-made habitats in Silesian Upland in southern Poland. Soil samples were collected from 5 sites in order to measure the contents of organic carbon, nitrogen, carbon/nitrogen ratio and percentage of organic matter, as well as the values of pH and electric conductivity. Lists of plants associated with Ptychoverpa bohemica were also prepared. Results of the investigation show that pH values of analysed soils are neutral to slightly acidic, they show negligible salinity, and the content of organic carbon, nitrogen and organic matter are higher in their upper levels. The floristic composition of patches with Ptychoverpa bohemica usually consists of species which are common in urban areas, such as apophytes and anthropophytes, for example: Betula pendula, Brachythecium rutabulum, Epipactis helleborine, Pinus sylvestris, Populus tremula, Quercus robur, Salix caprea and Sorbus aucuparia.
Six chironomid species: Paraboreochlus minutissimus (Strobl, 1894), Trissopelopia longimanus (Staeger 1839), Boreoheptagyia monticola (Serra-Tosio, 1964), Cricotopus (s.str.) similis Goetghebuer 1921, Heleniella serratosioi Ringe, 1976, Krenosmittia camptophleps (Edwards, 1929), were recorded in Czech Republic for the first time. The pupal exuviae were collected in July 2009 from Otava River in the vicinity of Rejštejn village in the central part of the Bohemian Forest. The notes on known distribution and ecology of the species are presented.
The paper presents new faunistic record of Schineriella schineri (Strobl, 1880) for Slovakia from Číčov oxbow lake. Details on finding and notes on distribution and ecology are given.
Records of 11 species of three families of acalyptrate Diptera, Micropezidae (4 species), Clusiidae (4) and Periscelididae (3) are given from Portugal. Seven species are new faunal additions to this country, viz. Neria cibaria (Linnaeus, 1761), Neria octoannulata (Strobl, 1899) (both Micropezidae), Clusiodes albimanus (Meigen, 1830), C. caledonicus (Collin, 1912), C. gentilis (Collin, 1912) (all Clusiidae), Periscelis (Myodris) piricercus Carles-Tolrá & Verdugo Páez, 2009 and P. (Periscelis) sp. n. near P. winnertzii Egger, 1862 (Periscelididae). Distribution and biology of all recorded species are reviewed and supplemented with new information based on Portuguese material and notes on the taxonomy and variability of some species are appended.
The article presents recent findings of epiphytic bryophytes from the Orthotrichaceae family in the Muránska planina National Park. Field surveys were carried out between 2008 and 2016. In total, 111 localities were visited. Altogether, 19 taxa from the Orthotrichaceae family were recorded - 8 of them are new for the territory of the National Park (Dorcadion affine var. bohemicum, D. rupestre, Orthotrichum diaphanum, O. patens, O. scanicum, O. stramineum, Pulvigera lyellii, and Ulota bruchii) and 1 as new for Slovakia (Dorcadion affine var. bohemicum). Eleven species are listed on the Red list of bryophytes of Slovakia – EX: Orthotrichum rogeri; CR: Nyholmiella gymnostoma, Orthotrichum patens, O. scanicum; VU: Dorcadion striatum, Ulota bruchii; NT: Dorcadion speciosum, Orthotrichum pallens, Pulvigera lyellii, Ulota crispa; DD: Orthotrichum stramineum. The most interesting findings are briefly discussed.
Niemodlin countryside (c. 300 km2) is situated in the south-western part of Opole Silesia, SW Poland. Forests occupy c. 40%, arable grounds – 1/3, and meadows and pastures – 7%. There are 31 fish-ponds with a total diked surface of 663 ha. The paper presents results of field investigations carried out during the years 2002-2007 and an analysis of changes in the breeding avifauna over the last 56 years. During the years 2002-2007, 123 breeding and 11 probably breeding bird species were recorded in this area. During the years 1962-2007 151 species were recorded as breeding residents; and additional five species – as probably breeding resident. The following species were recorded as breeding for the first time in 1962-2007: Haliaeetus albicilla, Larus canus, Motacilla cinerea, Saxicola torquata, Locustella luscinioides, Ficedula albicollis, Corvus corax and Carpodacus erythrinus. In the same period the following species became extinct: Podiceps nigricollis, Anas clypeata, Milvus milvus, and Tringa glareola. The following species increaed in numbers in 1962-2007: Coturnix coturnix, Grus grus, Columba oenas, Apus apus, Dryocopus martius, Dendrocopos medius, Motacilla cinerea, Saxicola torquata and Corvus corax. In the same period, Tachybaptus ruficollis, Podiceps cristatus, Podiceps grisegena, Ciconia ciconia, Aythya nyroca, Perdix perdix, Gallinago gallinago, Larus ridibundus, Tyto alba, Alcedo atthis, Picus viridis, Riparia riparia and Corvus cornix decreased in numbers. The areas with the highest concentration of rare and endangered species are postulated to be protected as nature reserves, landscape parks and other spatial forms of nature conservation.
The investigation of three streams in the Moravian part of the Javorníky Mts in 2003 and 2006–2009 brings the first records of Plecoptera in these mountains. A total of 28 species and were found (30 % of the recent fauna of the Czech Republic), among which species of the upper parts of streams predominate. This result corresponds to the nature of the habitat on which researches have been carried out. One endangered species (Leuctra cf. major), two vulnerable species (Dinocras cephalotes, Perla marginata) and one near threatened species (Leuctra quadrimaculata) were recorded. Comparing the recorded species to those of the neighbouring mountains, it can be assumed that the fauna of stoneflies of the Javorníky Mts may contain more than 40 species and can form a continuous transition between the Moravskoslezské Beskydy Mts and the Bílé Karpaty Mts (including the Vizovická vrchovina Highlands).
Collections of benthic organisms were obtained during previous Soviet research cruises in the Mediterranean Sea, 1974–1980. Material was collected by bottom grabs or trawls from the depths of 20-500m. Collecting stations were allocated in the Aegean, Adriatic, Tyrrhenian, Balearic, Alboran, and Ionian Seas, and between Sicily and Tunisia. Among decapod crustaceans collected, 8 species of portunid crabs were present, i.e., Liocarcinus. corrugatus (Pennant, 1777), L. depurator (Linnaeus, 1758), L. maculatus (Risso, 1827), L. navigator (Herbst, 1794), L. vernalis (Pennant, 1816), L. zariquieyi Gordon, 1968, Macropipus tuberculatus (Roux, 1830), and Bathynectes longipes (Risso, 1816). For two species, L. maculatus and L. zariquieyi, new distributional records are presented here. An extension of the known depth range is reported here for L. maculatus and L. vernalis.
The paper reports on finds of the invasive species Senecio inaequidens along motorways in Poland and Slovakia. The species was already mentioned in the floras of both countries but until recently there had been no reports from motorways there. In 2015, a large population of Senecio inaequidens was found along the A4 motorway in Poland. In 2013, it was collected along the D2 motorway in Slovakia. Intensive road traffic is probably the main vector of Senecio inaequidens invasion along motorways in Central Europe. Motor vehicles can carry the propagules over long distances. The newly recorded sites along the A4 in Poland and the D2 in Slovakia are part of the species’ invasion eastwards. It is assumed that Senecio inaequidens will continue to spread along motorways in both countries and in the region as a whole.
The paper presents information about habitat conditions of occurrence of the Ptychoverpa bohemica (Krombh.) Boud. fungus in man-made habitats in Silesian Upland in southern Poland. Soil samples were collected from 5 sites in order to measure the contents of organic carbon, nitrogen, carbon/nitrogen ratio and percentage of organic matter, as well as the values of pH and electric conductivity. Lists of plants associated with Ptychoverpa bohemica were also prepared. Results of the investigation show that pH values of analysed soils are neutral to slightly acidic, they show negligible salinity, and the content of organic carbon, nitrogen and organic matter are higher in their upper levels. The floristic composition of patches with Ptychoverpa bohemica usually consists of species which are common in urban areas, such as apophytes and anthropophytes, for example: Betula pendula, Brachythecium rutabulum, Epipactis helleborine, Pinus sylvestris, Populus tremula, Quercus robur, Salix caprea and Sorbus aucuparia.
Six chironomid species: Paraboreochlus minutissimus (Strobl, 1894), Trissopelopia longimanus (Staeger 1839), Boreoheptagyia monticola (Serra-Tosio, 1964), Cricotopus (s.str.) similis Goetghebuer 1921, Heleniella serratosioi Ringe, 1976, Krenosmittia camptophleps (Edwards, 1929), were recorded in Czech Republic for the first time. The pupal exuviae were collected in July 2009 from Otava River in the vicinity of Rejštejn village in the central part of the Bohemian Forest. The notes on known distribution and ecology of the species are presented.
The paper presents new faunistic record of Schineriella schineri (Strobl, 1880) for Slovakia from Číčov oxbow lake. Details on finding and notes on distribution and ecology are given.
Records of 11 species of three families of acalyptrate Diptera, Micropezidae (4 species), Clusiidae (4) and Periscelididae (3) are given from Portugal. Seven species are new faunal additions to this country, viz. Neria cibaria (Linnaeus, 1761), Neria octoannulata (Strobl, 1899) (both Micropezidae), Clusiodes albimanus (Meigen, 1830), C. caledonicus (Collin, 1912), C. gentilis (Collin, 1912) (all Clusiidae), Periscelis (Myodris) piricercus Carles-Tolrá & Verdugo Páez, 2009 and P. (Periscelis) sp. n. near P. winnertzii Egger, 1862 (Periscelididae). Distribution and biology of all recorded species are reviewed and supplemented with new information based on Portuguese material and notes on the taxonomy and variability of some species are appended.
The article presents recent findings of epiphytic bryophytes from the Orthotrichaceae family in the Muránska planina National Park. Field surveys were carried out between 2008 and 2016. In total, 111 localities were visited. Altogether, 19 taxa from the Orthotrichaceae family were recorded - 8 of them are new for the territory of the National Park (Dorcadion affine var. bohemicum, D. rupestre, Orthotrichum diaphanum, O. patens, O. scanicum, O. stramineum, Pulvigera lyellii, and Ulota bruchii) and 1 as new for Slovakia (Dorcadion affine var. bohemicum). Eleven species are listed on the Red list of bryophytes of Slovakia – EX: Orthotrichum rogeri; CR: Nyholmiella gymnostoma, Orthotrichum patens, O. scanicum; VU: Dorcadion striatum, Ulota bruchii; NT: Dorcadion speciosum, Orthotrichum pallens, Pulvigera lyellii, Ulota crispa; DD: Orthotrichum stramineum. The most interesting findings are briefly discussed.
Niemodlin countryside (c. 300 km2) is situated in the south-western part of Opole Silesia, SW Poland. Forests occupy c. 40%, arable grounds – 1/3, and meadows and pastures – 7%. There are 31 fish-ponds with a total diked surface of 663 ha. The paper presents results of field investigations carried out during the years 2002-2007 and an analysis of changes in the breeding avifauna over the last 56 years. During the years 2002-2007, 123 breeding and 11 probably breeding bird species were recorded in this area. During the years 1962-2007 151 species were recorded as breeding residents; and additional five species – as probably breeding resident. The following species were recorded as breeding for the first time in 1962-2007: Haliaeetus albicilla, Larus canus, Motacilla cinerea, Saxicola torquata, Locustella luscinioides, Ficedula albicollis, Corvus corax and Carpodacus erythrinus. In the same period the following species became extinct: Podiceps nigricollis, Anas clypeata, Milvus milvus, and Tringa glareola. The following species increaed in numbers in 1962-2007: Coturnix coturnix, Grus grus, Columba oenas, Apus apus, Dryocopus martius, Dendrocopos medius, Motacilla cinerea, Saxicola torquata and Corvus corax. In the same period, Tachybaptus ruficollis, Podiceps cristatus, Podiceps grisegena, Ciconia ciconia, Aythya nyroca, Perdix perdix, Gallinago gallinago, Larus ridibundus, Tyto alba, Alcedo atthis, Picus viridis, Riparia riparia and Corvus cornix decreased in numbers. The areas with the highest concentration of rare and endangered species are postulated to be protected as nature reserves, landscape parks and other spatial forms of nature conservation.