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FIGURE 1 in A new Cernosvitoviella species (Clitellata: Enchytraeidae) and its comparison with other Cernosvitoviella species from Sphagnum mires in Hungary
FIGURE 1. Spermathecae of Cernosvitoviella species. A. C. farkasi sp. n. B. C. aggtelekiensis. C. C. atrata. D. C. crassoductus. E. C. minor s. l. with small spermatheca. F. C. minor s. l. Scale bars 50 µm.
FIGURE 3 in A new Cernosvitoviella species (Clitellata: Enchytraeidae) and its comparison with other Cernosvitoviella species from Sphagnum mires in Hungary
FIGURE 3. Micrographs of Cernosvitoviella farkasi sp. n. A. Large sperm funnels (arrows, sv=seminal vesicle, e=egg). B. The wide dilatation of the sperm duct (the male pore with glands marked with arrows). C. Sperm funnels (short arrows) and the sperm ducts. D. Sperm ducts (male opening marked with arrow), in C and D, clearly visible that the wide parts of the ducts are conspicuous, refractile. E. Male pores with glands surrounding (arrow). F. Ectal widenings of the spermathecal ducts (arrows). G. Ectal widenings of the spermathecal ducts (black arrows) and the sphaerical bulb with sperm in them (white arrow). H. Epibiont on the body wall. A–D, F in vivo, E, G–H fixed, stained. Scale bars in A–F 50 µm, in G–H 20 µm.
FIGURE 2 in A new Cernosvitoviella species (Clitellata: Enchytraeidae) and its comparison with other Cernosvitoviella species from Sphagnum mires in Hungary
FIGURE 2. Micrographs of Cernosvitoviella farkasi sp. n. A. Brain and prostomial papillae (arrow). B. Prostomial papillae (arrows). C. Coelomocytes (arrows, e=egg). D. Coelomocytes in the coelom and outside the body (p=pygidium). E. Pars tumida in XVIII–XIX (arrows). F. Nephridium (arrow). G. Chloragogen cells behind the clitellum. H. Segments III–VII (ectal opening of spermathecae marked with black arrows, b=hemispherical bulb, long sack-like ampullae marked with white arrows). I. segments XI–XII (sperm funnels marked with white arrows, dilatation of sperm funnels marked with black arrows, m=male openings, epibionts on the body wall marked with short arrows). A fixed, stained, B–I in vivo. Scale bars 50 µm.
FIGURE 11 in A new Cernosvitoviella species (Clitellata: Enchytraeidae) and its comparison with other Cernosvitoviella species from Sphagnum mires in Hungary
FIGURE 11. Cernosvitoviella species, maximum likelihood (ML) trees of the ITS region (A), CO1 (B) and H3 genes (C). Bootstrap values greater than 50 are shown at the nodes. Accession codes of sequences with collection information are given in Table 2. A. ML tree of the ITS region based on 901 nucleotide positions. B. ML tree of the CO1 gene based on 500 nucleotide positions. C. ML tree of the H3 gene based on 218 nucleotide positions.
Hungary Synthetic Ecosystem
Hungary synthetic ecosystem dataset consisting of tables for persons and households. This dataset was created by the SPEW R Package using the following input data sources: GeoHive counts and IPUMS-I shapefiles and microdata.
Collared pratincole nest success in Hungary
<p>Agricultural intensification has affected wildlife across Europe, triggering steep declines and regional extinctions of farmland birds. Effective conservation activities are essential for the preservation of biodiversity in an agricultural landscape, but current efforts have not succeeded in halting these declines. Here we investigate a ground-nesting shorebird, the collared pratincole, <em>Glareola</em> <em>pratincola</em>, which has shifted its habitat use in Central Europe over the last 20 years from alkaline grasslands to intensively managed agricultural fields. We show that nesting success was different between three agricultural habitat types, with the highest nesting success in fallow lands and the lowest in row crops. Nesting success was also associated with the timing of breeding and breeding density, as nests produced early in the breeding season and those in high-breeding-density areas hatched more successfully than those produced later in the season and at low density. We implemented direct conservation measures including marking nests and negotiating with farmers to avoid cultivating the field between nest markers, controlling nest predators, and, most recently, creating suitable nesting sites and foraging areas for pratincoles. As a result of these conservation actions, nest survival increased from 11.2% to 83.5% and the size of the breeding population increased from 13 to 56 pairs during 2012–2021. Thus, we show that agricultural landscapes can continue to provide important habitats, and targeted conservation actions have the potential to reverse the declines of farmland species.</p>
Chapel - Baranyahídvég - Hungary (pointcloud)
Source: Objaverse 1.0 / Sketchfab
Fig. 102 in FREE-LIVING NEMATODES OF HUNGARY (NEMATODA ERRANTIA)
Fig. 102. Enchodelus macrodorus (de Man, 1880). a. anterıor end: b: female posterior end; c: male posterior end
Fig. 101 in FREE-LIVING NEMATODES OF HUNGARY (NEMATODA ERRANTIA)
Fig. 101. Longidorella tredecima (Andrassy, 1964). a: anterior end; b: vulval region; c: female posterior end.
FIGURE 2 in A new species of the vitismin cockroach genus Perspicuus Koubová, 2020 from the Late Cretaceous (Santonian) of Hungary
FIGURE 2. Perspicuus csincsii sp. n. a) photo of maxillary palp. b) line drawing of maxillary palp. c) photograph of partially preserved antenna. d) line drawing of antennal segments. e) habitus in dorsal view. f) indicated fore leg under the ventral side of the body. g) line drawing of the claws and arolium of the same leg. h) part of hind leg in dorsal aspect. i) line drawing of suggested middle leg in ventral aspect. j) cercus in dorsal aspect. k) line drawing of the cercus. Figures (a) and (b) have no scale bars, as these parts were destroyed during preparation and are no longer available for further examination.
Subspecies and Distribution. N. p. procyonoides Gray, 1834 — W & SW China and N Indochina. N. p. albus Hornaday, 1904 — Japan (Hokkaido). N. p. koreensis Mori, 1922 — Korean Peninsula. N. p. orestes Thomas, 1923 — C & S China. N. p. ussuriensis Matschie, 1907 — NE China, E Mongolia, and SE Russia. N. p. viverrinus Temminck, 1839 — Japan. Introduced (ussuriensis) to the Baltic states, Belarus, Bulgaria, Czech Republic, Finland, Germany, Hungary, Moldova, Poland, Romania, W Russia, Serbia, Slovakia, Sweden, and Ukraine, occasionally seen in Austria, Bosnia, Denmark, France, the Netherlands, Norway, Slovenia, and Switzerland. in Canidae
Subspecies and Distribution. N. p. procyonoides Gray, 1834 — W & SW China and N Indochina. N. p. albus Hornaday, 1904 — Japan (Hokkaido). N. p. koreensis Mori, 1922 — Korean Peninsula. N. p. orestes Thomas, 1923 — C & S China. N. p. ussuriensis Matschie, 1907 — NE China, E Mongolia, and SE Russia. N. p. viverrinus Temminck, 1839 — Japan. Introduced (ussuriensis) to the Baltic states, Belarus, Bulgaria, Czech Republic, Finland, Germany, Hungary, Moldova, Poland, Romania, W Russia, Serbia, Slovakia, Sweden, and Ukraine, occasionally seen in Austria, Bosnia, Denmark, France, the Netherlands, Norway, Slovenia, and Switzerland.
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest. in Suidae
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest.
Subspecies and Distribution. N. p. procyonoides Gray, 1834 — W & SW China and N Indochina. N. p. albus Hornaday, 1904 — Japan (Hokkaido). N. p. koreensis Mori, 1922 — Korean Peninsula. N. p. orestes Thomas, 1923 — C & S China. N. p. ussuriensis Matschie, 1907 — NE China, E Mongolia, and SE Russia. N. p. viverrinus Temminck, 1839 — Japan. Introduced (ussuriensis) to the Baltic states, Belarus, Bulgaria, Czech Republic, Finland, Germany, Hungary, Moldova, Poland, Romania, W Russia, Serbia, Slovakia, Sweden, and Ukraine, occasionally seen in Austria, Bosnia, Denmark, France, the Netherlands, Norway, Slovenia, and Switzerland. in Canidae
Subspecies and Distribution. N. p. procyonoides Gray, 1834 — W & SW China and N Indochina. N. p. albus Hornaday, 1904 — Japan (Hokkaido). N. p. koreensis Mori, 1922 — Korean Peninsula. N. p. orestes Thomas, 1923 — C & S China. N. p. ussuriensis Matschie, 1907 — NE China, E Mongolia, and SE Russia. N. p. viverrinus Temminck, 1839 — Japan. Introduced (ussuriensis) to the Baltic states, Belarus, Bulgaria, Czech Republic, Finland, Germany, Hungary, Moldova, Poland, Romania, W Russia, Serbia, Slovakia, Sweden, and Ukraine, occasionally seen in Austria, Bosnia, Denmark, France, the Netherlands, Norway, Slovenia, and Switzerland.
Distribution. Mediterranean Europe in N Spain, S France, W & S Switzerland, N Italy, S Austria, Slovenia, Hungary, Croatia, N Bosnia and Herzegovina, and NE Serbia. in Cricetidae
Distribution. Mediterranean Europe in N Spain, S France, W & S Switzerland, N Italy, S Austria, Slovenia, Hungary, Croatia, N Bosnia and Herzegovina, and NE Serbia.
FIGURE 1 in A new species of the genus Curculio Linnaeus, 1758 (Coleoptera: Curculionidae) from Hungary and the Balkan Peninsula
FIGURE 1. Habitus of Curculio species. Curculio gyongyiae a, b holotype male dorsal and lateral view; c, d paratype female dorsal and lateral view; C. propinquus: e, f non type male dorsal and lateral view; g, h non type female dorsal and lateral view; C. elephas: i, j non type male dorsal and lateral view; k, l non type female dorsal and lateral view. Scale bar: 5 mm. Scale bar: 5 mm.
FIGURE 2 in A new species of the genus Curculio Linnaeus, 1758 (Coleoptera: Curculionidae) from Hungary and the Balkan Peninsula
FIGURE 2. Male terminalia of Curculio species. Penis median lobe ventral, lateral view and median lobe tip of Curculio gyongyiae: a, b, c; C. propinquus; d, e, f; C. elephas; g, h, i. Spiculum gastrale of C. gyongyiae: j; C. propinquus: k. Scale bar: 1 mm. Not to scale: c, f, i.
FIGURE 5 in A new species of the genus Curculio Linnaeus, 1758 (Coleoptera: Curculionidae) from Hungary and the Balkan Peninsula
FIGURE 5. Habitats of Curculio gyongyiae in Hungary. Pilisszántó, Pilistető: a; Pilisborosjenő, Nagy-Kevély: b; Vértestolna, Pes-kő: c–d.
FIGURE 3 in A new species of the genus Curculio Linnaeus, 1758 (Coleoptera: Curculionidae) from Hungary and the Balkan Peninsula
FIGURE 3. Male terminalia of Curculio species. Spiculum gastrale of C. elephas; a. Tegmen of C. gyongyiae: b; C. propinquus; c; C. elephas: d. Female genitalia of Curculio species. Spiculum ventrale of C. gyongyiae: e; C. propinquus: f; C. elephas: g. Spermatheca of C. gyongyiae: h; C. propinquus: i; C. elephas: j. Scale bar: 1 mm, (except h, i, j: 0.3 mm).
Subspecies and Distribution. S.a.alpinusSchinz,1837—SEFrance,Switzerland,NItaly,C&SGermany,SWCzechRepublic,Austria,Slovenia,NWHungary,Croatia,BosniaandHerzegovina,Serbia,Montenegro,andNAlbania. S.a.hercynicusG.S.Miller,1909—NGermany(Harz);possiblyextinct. S. a. tatricus Kratochvil & Rosicky, 1952 — N & E Czech Republic, Slovakia, S Poland, W Ukraine, NE Hungary, and Romania. in Soricidae
Subspecies and Distribution. S.a.alpinusSchinz,1837—SEFrance,Switzerland,NItaly,C&SGermany,SWCzechRepublic,Austria,Slovenia,NWHungary,Croatia,BosniaandHerzegovina,Serbia,Montenegro,andNAlbania. S.a.hercynicusG.S.Miller,1909—NGermany(Harz);possiblyextinct. S. a. tatricus Kratochvil & Rosicky, 1952 — N & E Czech Republic, Slovakia, S Poland, W Ukraine, NE Hungary, and Romania.
Distribution. Endemic to SE Europe (Austria, Slovakia, Hungary, Croatia, Bosnia and Herzegovina, Serbia, Montenegro, Albania, Greece, Romania, Bulgaria, Moldova, Ukraine, and Russia). in Muridae
Distribution. Endemic to SE Europe (Austria, Slovakia, Hungary, Croatia, Bosnia and Herzegovina, Serbia, Montenegro, Albania, Greece, Romania, Bulgaria, Moldova, Ukraine, and Russia).
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Annotated Behaviour and Observability Dataset (ABODe)
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