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Figure 4. A cove with shallow water near Ponte Porton with 14 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia

Figure 4. A cove with shallow water near Ponte Porton with 14 individuals of Microcondylaea bonellii (26.9.2009).

Figure 3 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia

Figure 3. Numbers of shells of Unio mancus (blue) and Microcondylaea bonelli at the different sites (red).

Fig. 2 and 3 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia

Fig. 2 and 3 give the results of my surveys in river Mirna in 2009 to 2016. In the upper part of the river from the city of Buzet to the confluence with Butoniga the artificially straightened riverbed is dominated by coarse gravel and shows ± rapid current. Although Microcondylaea was recorded from this part of the river near Istarske Teplice (Fischer 1999) no shells or living specimens were found actually. Populations of Unio mancus were mainly found in tributaries like Bračana and drenches, less frequently in the riverbed of upper Mirna. Between 2009 and 2016 the Mirna-riverbed was reconstructed in several places, eroded banks with coves and fine sand substrate were replaced by blocks of stone and the riverbed straightened again. Thus many suitable habitats and eventually existing mussels-populations were destroyed, so much the worse as heavy machines were driving in the riverbed over many weeks for the construction works and mobilized the substrate, which led to high accumulations of fine sediment in the lower part of the river, especially in parts with low current and coves which were inhabited by Microcondylaea.

Figure 1 in Populations of Microcondylaea bonellii (Férussac 1827), Unionidae - an european freshwater mussel at rapid decline - and Unio mancus in Istria, Croatia

Figure 1. Map of known living populations of Microcondylaea bonelli in Slovenia (grey) and Italy (yellow) from http://art17.eionet.europa.eu/article17/reports2012/species/summary/. Populations in Croatia (red) added by the author.

opencc-by-4.0Oct 2018View details →

Figure 1. Adult Trocheta haskonis Grosser, 2000 from Banja Luka. A-B in Monster from the Vault: a new finding of one of the largest European leech Trocheta haskonis Grosser, 2000 from Bosnia and Herzegovina

Figure 1. Adult Trocheta haskonis Grosser, 2000 from Banja Luka. A-B Living specimens; C-D Sampling site: utility vault near in the village Prijakovci, Banja Luka, photographed in summer 2018. Photos by G. Šukalo.

opencc-by-4.0Oct 2018View details →

Figure 2 in Monster from the Vault: a new finding of one of the largest European leech Trocheta haskonis Grosser, 2000 from Bosnia and Herzegovina

Figure 2. Adult Trocheta haskonis from the locus typicus and its earth-worm prey. Photo by C. Grosser.

opencc-by-4.0Jul 2024View details →

Sensitivity of fire weather indices, fuel sticks and satellite observations to fuel moisture content in Central European forests - Data

This data repository contains datasets for destructively measured fuels of different types (FMC_insitu), meteorological data including 10-hour fuel stick measurements (FWS_30min) and calculated fire weather index components (FWS_FWI_24h) for four different sites in the Tharandt forest and Saxon Switzerland National Park in the Free State of Saxony (Germany) during the years 2022 (only DE-Tha) and 2023 (all four sites). The provided folders contain .csv files for each study site. Meteorological data in 30min for DE-Tha can be derived from the ICOS data portal (https://data.icos-cp.eu/portal/). For the remaining three sites (DE-BLB, DE-BWB, DE-SHW), past and recent data can be viewed via EMS Brno (e.g., http://www.emsbrno.cz/p.axd/en/Beech__Landberg.TU__DRESDEN.html). Upon request, the authors can share the data.  FMC_insitu: Destructively sampled fuel moisture content of different fuel types. FWS_30min: Original measurements from the fire weather stations in 30 min time steps FWS_FWI_24h: Measurements from fire weather stations in 24h time steps and the calculated fire weather index and its components. As requested for calculation of the FWI, meteorological variables are used at 13:00 (UTC), while PREC and PBC are the 24h sum prior to 13:00.  readme.txt: Description of repository content and the variables provided within the .csv files. stations.csv: Contains the coordinates and a short description of the study sites.

Figure 8 in Ontogenetic development of the European basal aquatic turtle Pleurosternon bullockii (Paracryptodira, Pleurosternidae)

Figure 8. Shape differences of the entoplastron of Pleurosternon bullockii (Paracryptodira, Pleurosternidae), taking into account specimens from both the Tithonian (Late Jurassic) and Berriasian (Early Cretaceous) of England. (a) Principal component analysis (PCA). Wireframes indicate the main shape changes in each PC; the light blue concerns the average shape, whereas the dark blue is the shape variance related to the extreme of variation along the axis. (b) Transformation grids to visualize shape deformation relative to the first three principal components. Abbreviations: C, CAMSM; D, DORCM; N, NHMUK.

Figure 7 in Ontogenetic development of the European basal aquatic turtle Pleurosternon bullockii (Paracryptodira, Pleurosternidae)

Figure 7. Shape differences of the anterior plastral lobe of Pleurosternon bullockii (Paracryptodira, Pleurosternidae), taking into account specimens from the Berriasian (Early Cretaceous) of Swanage (Dorset, England). (a) Principal component analysis (PCA). Wireframes indicate the main shape changes in each PC; the light blue concerns the average shape, whereas the dark blue is the shape variance related to the extreme of variation along the axis. (b) Transformation grids to visualize shape deformation relative to the first three principal components. Abbreviation: N, NHMUK.

Figure 1 in Ontogenetic development of the European basal aquatic turtle Pleurosternon bullockii (Paracryptodira, Pleurosternidae)

Figure 1. Shells of juvenile specimens of Pleurosternon bullockii (Paracryptodira, Pleurosternidae), from the Berriasian (Early Cretaceous) of Swanage (Dorset, England) (a, b, f), and detail of the carapace ornamentation of juvenile (c, e) and adult (d) individuals. (a–c) NHMUK 48262, shell in dorsal (a) and ventral (b) views, as well as detail of the ornamentation of the nuchal (c). (d) Detail of the ornamentation of the nuchal of NHMUK OR 28618 (see fig. 3B in Guerrero and PØrez-García, 2021). (e) Detail of the ornamentation of the central area of the carapace of NHMUK 48263a (see Fig. 2a). (f) NHMUK 48345, in dorsal view. Scale bars equal 2 cm in (a), (b) and (f) and 1 cm in (c)–(e).

Figure 3 in Ontogenetic development of the European basal aquatic turtle Pleurosternon bullockii (Paracryptodira, Pleurosternidae)

Figure 3. Partial shells and isolated plates of juvenile specimens of Pleurosternon bullockii (Paracryptodira, Pleurosternidae), from the Berriasian (Early Cretaceous) of Swanage (Dorset, England). (a) NHMUK 48354, in dorsal (carapace) and ventral (plastron) views. (b– c) NHMUK 48264, in dorsal (b) and ventral (c) views. (d) NHMUK 48355, in ventral view. (e) NHMUK 48352, costal plates in dorsal view. (f) NHMUK 48346, hyoplastron in dorsal view. Scale bars equal 2 cm.

Figure 5 in Ontogenetic development of the European basal aquatic turtle Pleurosternon bullockii (Paracryptodira, Pleurosternidae)

Figure 5. Shape differences of the nuchal of Pleurosternon bullockii (Paracryptodira, Pleurosternidae), taking into account specimens from the Berriasian (Early Cretaceous) of Swanage (Dorset, England). (a–b) Principal component analysis (PCA). Wireframes indicate the main shape changes in each PC; the light blue concerns the average shape, whereas the dark blue is the shape variance related to the extreme of variation along the axis. (c) Transformation grids to visualize shape deformation relative to the first three principal components. Abbreviations: C, CAMSM; D, DORCM; N, NHMUK.

opencc-by-4.0Nov 2010View details →

Fig. 2 Phylogenetic tree representing relationships within Discodorididae. The latter contains about 400 species and 40 in A warning for ecologists and conservation biologists using species checklists: How the European marine fauna 'lost' all of its 16 Discodoris species (Mollusca: Gastropoda)

Fig. 2 Phylogenetic tree representing relationships within Discodorididae. The latter contains about 400 species and 40 genera, only some of which are mentioned here, with special emphasis on the genera that contain species originally described in Discodoris. Tree terminal taxa are labeled with the specific epithet followed by the generic name of the original combination in parenthesis. The current generic names are given on the right side of the braces indicating the (few) species per genus mentioned. Assignment of a generic name to a clade is based on a type species that belongs to that clade (e.g., Discodoris boholiensis is the type species of Discodoris). All genera correspond to clades, with the exception of "Montereina", a metaphyletic group at the base of Discodorididae for which no autapomorphic, diagnostic features could be found. For additional information on phylogenetic analyses, authorship of species names, etc., see Dayrat (2010a)

opencc-by-4.0Nov 2010View details →

Fig. 1 Live discodorid sea slugs, dorsal views. a Peltodoris atromaculata Bergh, 1880. b Discodoris boholiensis Bergh, 1877. c in A warning for ecologists and conservation biologists using species checklists: How the European marine fauna 'lost' all of its 16 Discodoris species (Mollusca: Gastropoda)

Fig. 1 Live discodorid sea slugs, dorsal views. a Peltodoris atromaculata Bergh, 1880. b Discodoris boholiensis Bergh, 1877. c Tayuva lilacina (Gould 1852). d "Montereina" aurila (Marcus and

opencc-by-4.0Dec 2023View details →

Fig. 1 in The effects of short-term climate change on the range of species: the case of the expanding European dwarf mantis Ameles spallanzania in northern Italy (Mantodea: Amelidae)

Fig. 1 – Distribution of Ameles spallanzania in Italy across a, past period and b, current period. Confirmed data refer to already known presence cells in the previous time interval.

opencc-by-sa-4.0Jan 2022View details →

Comparison of Drug Prescribing Before and During the COVID-19 Pandemic - A Cross-national European Study. Pharmaceuticals Consumption data

Data and code supporting the article: Comparison of Drug Prescribing Before and During the COVID-19 Pandemic - A Cross-national European Study    Prescription data from January 2017 to March 2021 for the Czech Republic, Germany, Lithuania, Slovenia, Spain (Catalonia), Sweden, and the United Kingdom (Scotland). Data include the codes of the Anatomical-Therapeutic-Chemical classification (ATC) and corresponding numbers of dispensed defined daily doses (DDDs) and packs, aggregated by country, month and ATC. For more information, see the accompanying document ReadMe.txt.

Fig. 1 in Short communication An evidence of asp viper (Vipera aspis) consumption by a western European hedgehog (Erinaceus europaeus) on Elba Island (Italy)

Fig. 1 - Map of Italy. The red arrow points to the Elba Island. / Mappa d'Italia. La freccia rossa indica l'Isola d'Elba. (Google Earth. Data SIO, NOAA, U.S. Navy, NGA, GEBCO. Image Landsat / Copernicus).

Fig. 2 - A in Short communication An evidence of asp viper (Vipera aspis) consumption by a western European hedgehog (Erinaceus europaeus) on Elba Island (Italy)

Fig. 2 - A hedgehog consuming an asp viper on Elba. / Un riccio che consuma un aspide all'Elba. (Photo/foto: Walter Costa).

Fig. 2 in The western European hedgehog Erinaceus europaeus L. 1758 on San Pietro Island (southern Sardinia, Italy) and an updated review of its presence on the Italian small islands

Fig. 2 - The small Italian islands with evidence of western European hedgehog presence. Thick-bordered circles: probable occurrence of stable populations; thin-bordered circles: only occasional presence of individuals (low probability of short-term persistence). See Tab. 2 for details. / Evidenze di presenza di riccio europeo occidentale nelle piccole isole italiane. Cerchi con bordo spesso: probabile presenza di popolazioni stabili; cerchi con bordo sottile: probabile presenza di singoli individui (bassa probabilità di persistenza a breve termine). Vedasi Tab. 2 per dettagli. 1) Elba; 2) Capraia; 3) Pianosa; 4) Alicudi; 5) Salina; 6) Favignana; 7) Ustica; 8) Procida; 9) Vivara; 10) Capraia; 11) La Maddalena; 12) Asinara; 13) San Pietro.

Fig. 1 in The western European hedgehog Erinaceus europaeus L. 1758 on San Pietro Island (southern Sardinia, Italy) and an updated review of its presence on the Italian small islands

Fig. 1 - The study area (San Pietro Island, Sulcis archipelago; South Sardinia) with the evidence of presence of western European hedgehog. Black circles: direct observations; grey circles: indirect data. See Table 1 for details and numbers. / L'area di studio (Isola di San Pietro, arcipelago del Sulcis; Sardegna meridionale) con i siti di presenza del riccio europeo occidentale. Cerchi neri: osservazione dirette; cerchi grigi: dati indiretti. Vedere Tabella 1 per dettagli e numerazione.