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14 results for “Mixed Distribution”
Data from: Identifying priority areas for spatial management of mixed fisheries using ensemble of multi-species distribution models. Panzeri D. et al., 2023, Fish and Fisheries
<p>Panzeri D.<sup>1</sup>, Russo T., Arneri E., Carlucci R., Cossarini G., Isajlović I., Krstulović Šifner S., Manfredi C., Masnadi F., Reale M., Scarcella G., Solidoro C., Spedicato M.T., Vrgoč N., W. Zupa, Libralato S<sup>2</sup>.</p> <p><sup>1 </sup>dpanzeri@ogs.it<br> <sup>2 </sup>slibralato@ogs.it</p> <p>Spatial fisheries management is widely used to reduce overfishing, rebuild stocks, and protect biodiversity. However, the effectiveness and optimization of spatial measures depend on accurately identifying ecologically meaningful areas, which can be difficult in mixed fisheries. To apply a method generally to a range of target species, we developed an ensemble of species distribution models (e-SDM) that combines general additive models, generalized linear mixed models, random forest, and gradient-boosting machine methods in a training and testing protocol. The e-SDM was used to integrate density indices from two scientific bottom trawl surveys with the geopositional data, relevant oceanographic variables from the three-dimensional physical-biogeochemical operational model, and fishing effort from the vessel monitoring system. The determined best distributions for juveniles and adults are used to determine hot spots of aggregation based on single or multiple target species. We applied e-SDM to juvenile and adult stages of 10 marine demersal species representing 60% of the total demersal landings in the central areas of the Mediterranean Sea. Using the e-SDM results, hot spots of aggregation and grounds potentially more selective were identified for each species and for the target species group of otter trawl and beam trawl fisheries. The results confirm the ecological appropriateness of existing fishery restriction areas and support the identification of locations for new spatial management measures.</p> <p>Data (csv) for Panzeri et al. 2023</p> <p>1. <a href="https://zenodo.org/api/files/0b1b7af4-6a3b-481d-8d5f-57cf02d20eaa/Ensemble_density_F%26F_D.Panzeri_et_al_2023.csv">Ensemble_density_F&F_D.Panzeri_et_al_2023.csv: CSV file with density values (column pred) in terms of number of individuals (log N/km2) for each species (column sp) and life stage (column age) for each grid cell (X = longitude and Y = latitude).</a> </p> <p>2. <a href="https://zenodo.org/api/files/0b1b7af4-6a3b-481d-8d5f-57cf02d20eaa/Ensemble_density_F%26F_D.Panzeri_et_al_2023.csv">Getis_hotspot_F&F_D.Panzeri_et_al_2023.csv: CSV file with Getis ord Gi* values (column Gi) derived from the previous file 1, developed for each species and life stage for each grid cell (X = longitude and Y = latitude).</a></p> <p>3. <a href="https://zenodo.org/api/files/0b1b7af4-6a3b-481d-8d5f-57cf02d20eaa/Ensemble_density_F%26F_D.Panzeri_et_al_2023.csv">Multispecies_HotSpot_F&F_D.Panzeri_et_al_2023.csv: Frequency map expressed as the number of species for each grid cell (column freq) that has the hotspot (previous file 2) above the third quartile.</a></p> <p> </p> <p> </p>
Surgical case mixes and distributions of perioperative surgical process durations for German hospitals
<p>The data set consists of parameters of distributions of perioperative surgical process durations in German hospitals subdivided by the level of care, the surgical specialty, patient type (in- or outpatient), and the procedure’s main OPS code. We consider the following processes: anesthesia induction time, anesthesia emergence time, surgical lead-in, incision-to-closure time, surgical lead-out, and closure-to-incision time (as described in the German Perioperative Procedural Time Glossary). In addition, we provide the number of cases (classified by the procedure’s main OPS code) treated in one year per level of care, surgical specialty, and patient type (in- or outpatient).</p> <p>The supplied data set is the result of processing the 2019 surgical process data set from the Operating Room benchmarking program of German-speaking countries provided by the company digmed GmbH. In total, we considered 2,035,126 recorded surgeries from 212 different hospitals. The data set was created and published to facilitate and promote research on Operating Room planning in the field of Operations Research. It can be used for generating specific problem instances or benchmark sets for Operating Room planning problems.</p> <p> </p> <p> </p>
Impacts of representing heterogeneous distribution of cloud liquid and ice on phase partitioning of Arctic mixed-phase clouds with NCAR CAM5
<p>The model simulation outputs for the paper "Impacts of representing heterogeneous distribution of cloud liquid and ice on phase partitioningof Arctic mixed-phase clouds with NCAR CAM5".</p>
Data from: Do sperm really compete and do eggs ever have a choice? Adult distribution and gamete mixing influence sexual selection, sexual conflict, and the evolution of gamete recognition proteins in the sea
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Dataset S2: Global Synechococcus pigment type distribution from metagenomes with co-located mixed layer depths and sea surface properties
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Subspecies and Distribution. V. v. vulpes Linnaeus, 1758 — N Europe (Scandinavia). V. v. abietorum Merriam, 1900 — SW Canada (Alberta & British Columbia). V. v. aegyptiacus Sonnini, 1816 — Egypt, Israel, and Lybia. V. v. alascensis Merriam, 1900 — Alaska and NW Canada (NW Territories & Yukon). V. v. alpheraky: Satunin, 1906 — Kazakhstan. V. v. anatolica Thomas, 1920 — Turkey. V. v. arabica Thomas, 1902 — Arabian peninsula. V. v. atlantica Wagner, 1841 — Algeria (forested Atlas Mts). V. v. bangsi Merriam, 1900 — NE Canada (Labrador). V. v. barbara Shaw, 1800 — NW Africa (Barbary Coast). V. v. beringiana Middendorff, 1875 — NE Siberia (shore of Bering Strait). V. v. cascadensis Merriam, 1900 — NW USA (Cascade Mountains, Oregon & Washington). V. v. caucasica Dinnik, 1914 — SW Russia (Caucasus). V. v. crucigera Bechstein, 1789 — Europe through N & C Russia. V. v. daurica Ognev, 1931 — E Russia (Amur, Siberia & Transbaikalia). V.v. deletrix Bangs, 1898 — NE Canada (Newfoundland). V. v. dolichocrania Ognev, 1926 — SE Siberia (S Ussuri). V. v. flavescens Gray, 1843 — N Iran. V. v. fulva Desmarest, 1820 — E USA. V. v. griffith: Blyth, 1854 — Afghanistan and N Pakistan. V.v. harrimani Merriam, 1900 — Alaska (Kodiak I). V. v. hoole Swinhoe, 1870 — S China (Fujian to Sichuan). V. v. ichnusae G. S. Miller, 1907 — Corsica and Sardinia. V. v. induta G. S. Miller, 1907 — Cyprus. V. v. jakutensis Ognev, 1923 — E Siberia (S of Yakutsk). V. v. japonica Gray, 1868 — Japan. V. v. karagan Erxleben, 1777 — Mongolia, Kazakhstan, and Kirgizstan. V. v. kenaiensis Merriam, 1900 — Alaska (Kenai Peninsula). V. v. kurdistanica Satunin, 1906 — Armenia and NE Turkey. V. v. macroura Baird, 1852 — USA (Mountain States). V. v. montana Pearson, 1836 — Himalayas form China (Yunnan) to C Pakistan. V. v. mecator Merriam, 1900 — SW USA (California & Nevada). V_ v. ochroxantha Ognev, 1926 — E Russian Turkestan, Aksai, Kirgizstan, Semirechie. V. v. palaestina Thomas, 1920 —Jordan and Lebanon. V.v. peculiosa Kishida, 1924 — Korea. V. v. pusilla Blyth, 1854 — NW India to Irak. V.v. regalis Merriam, 1900 — N Great Plains of Canada and USA. V. v. rubricosa Bangs, 1898 — E Canada. V.v. schrencki Kishida, 1924 — N Japan (Hokkaido) and NE Russia (Sakhalin). V. v. silacea G. S. Miller, 1907 — Iberian Peninsula. V.v. splendidissima Kishida, 1924 — E Russia (N & C Kurile Is). V. v. stepensis Brauner, 1914 — steppes of S Russia. V. v. tobolica Ognev, 1926 — Russia (lower basin of Ob River) V. v. tschiliensis Matschie, 1907 — NE China. Foxes of European origin were introduced into E USA and Canada in the 17" century, subsequently mixed with local subspecies. Also introduced to Australia in 1800s, and the Falkland Islands (Malvinas). in Canidae
Subspecies and Distribution. V. v. vulpes Linnaeus, 1758 — N Europe (Scandinavia). V. v. abietorum Merriam, 1900 — SW Canada (Alberta & British Columbia). V. v. aegyptiacus Sonnini, 1816 — Egypt, Israel, and Lybia. V. v. alascensis Merriam, 1900 — Alaska and NW Canada (NW Territories & Yukon). V. v. alpheraky: Satunin, 1906 — Kazakhstan. V. v. anatolica Thomas, 1920 — Turkey. V. v. arabica Thomas, 1902 — Arabian peninsula. V. v. atlantica Wagner, 1841 — Algeria (forested Atlas Mts). V. v. bangsi Merriam, 1900 — NE Canada (Labrador). V. v. barbara Shaw, 1800 — NW Africa (Barbary Coast). V. v. beringiana Middendorff, 1875 — NE Siberia (shore of Bering Strait). V. v. cascadensis Merriam, 1900 — NW USA (Cascade Mountains, Oregon & Washington). V. v. caucasica Dinnik, 1914 — SW Russia (Caucasus). V. v. crucigera Bechstein, 1789 — Europe through N & C Russia. V. v. daurica Ognev, 1931 — E Russia (Amur, Siberia & Transbaikalia). V.v. deletrix Bangs, 1898 — NE Canada (Newfoundland). V. v. dolichocrania Ognev, 1926 — SE Siberia (S Ussuri). V. v. flavescens Gray, 1843 — N Iran. V. v. fulva Desmarest, 1820 — E USA. V. v. griffith: Blyth, 1854 — Afghanistan and N Pakistan. V.v. harrimani Merriam, 1900 — Alaska (Kodiak I). V. v. hoole Swinhoe, 1870 — S China (Fujian to Sichuan). V. v. ichnusae G. S. Miller, 1907 — Corsica and Sardinia. V. v. induta G. S. Miller, 1907 — Cyprus. V. v. jakutensis Ognev, 1923 — E Siberia (S of Yakutsk). V. v. japonica Gray, 1868 — Japan. V. v. karagan Erxleben, 1777 — Mongolia, Kazakhstan, and Kirgizstan. V. v. kenaiensis Merriam, 1900 — Alaska (Kenai Peninsula). V. v. kurdistanica Satunin, 1906 — Armenia and NE Turkey. V. v. macroura Baird, 1852 — USA (Mountain States). V. v. montana Pearson, 1836 — Himalayas form China (Yunnan) to C Pakistan. V. v. mecator Merriam, 1900 — SW USA (California & Nevada). V_ v. ochroxantha Ognev, 1926 — E Russian Turkestan, Aksai, Kirgizstan, Semirechie. V. v. palaestina Thomas, 1920 —Jordan and Lebanon. V.v. peculiosa Kishida, 1924 — Korea. V. v. pusilla Blyth, 1854 — NW India to Irak. V.v. regalis Merriam, 1900 — N Great Plains of Canada and USA. V. v. rubricosa Bangs, 1898 — E Canada. V.v. schrencki Kishida, 1924 — N Japan (Hokkaido) and NE Russia (Sakhalin). V. v. silacea G. S. Miller, 1907 — Iberian Peninsula. V.v. splendidissima Kishida, 1924 — E Russia (N & C Kurile Is). V. v. stepensis Brauner, 1914 — steppes of S Russia. V. v. tobolica Ognev, 1926 — Russia (lower basin of Ob River) V. v. tschiliensis Matschie, 1907 — NE China. Foxes of European origin were introduced into E USA and Canada in the 17" century, subsequently mixed with local subspecies. Also introduced to Australia in 1800s, and the Falkland Islands (Malvinas).
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. V. v. vulpes Linnaeus, 1758 — N Europe (Scandinavia). V. v. abietorum Merriam, 1900 — SW Canada (Alberta & British Columbia). V. v. aegyptiacus Sonnini, 1816 — Egypt, Israel, and Lybia. V. v. alascensis Merriam, 1900 — Alaska and NW Canada (NW Territories & Yukon). V. v. alpheraky: Satunin, 1906 — Kazakhstan. V. v. anatolica Thomas, 1920 — Turkey. V. v. arabica Thomas, 1902 — Arabian peninsula. V. v. atlantica Wagner, 1841 — Algeria (forested Atlas Mts). V. v. bangsi Merriam, 1900 — NE Canada (Labrador). V. v. barbara Shaw, 1800 — NW Africa (Barbary Coast). V. v. beringiana Middendorff, 1875 — NE Siberia (shore of Bering Strait). V. v. cascadensis Merriam, 1900 — NW USA (Cascade Mountains, Oregon & Washington). V. v. caucasica Dinnik, 1914 — SW Russia (Caucasus). V. v. crucigera Bechstein, 1789 — Europe through N & C Russia. V. v. daurica Ognev, 1931 — E Russia (Amur, Siberia & Transbaikalia). V.v. deletrix Bangs, 1898 — NE Canada (Newfoundland). V. v. dolichocrania Ognev, 1926 — SE Siberia (S Ussuri). V. v. flavescens Gray, 1843 — N Iran. V. v. fulva Desmarest, 1820 — E USA. V. v. griffith: Blyth, 1854 — Afghanistan and N Pakistan. V.v. harrimani Merriam, 1900 — Alaska (Kodiak I). V. v. hoole Swinhoe, 1870 — S China (Fujian to Sichuan). V. v. ichnusae G. S. Miller, 1907 — Corsica and Sardinia. V. v. induta G. S. Miller, 1907 — Cyprus. V. v. jakutensis Ognev, 1923 — E Siberia (S of Yakutsk). V. v. japonica Gray, 1868 — Japan. V. v. karagan Erxleben, 1777 — Mongolia, Kazakhstan, and Kirgizstan. V. v. kenaiensis Merriam, 1900 — Alaska (Kenai Peninsula). V. v. kurdistanica Satunin, 1906 — Armenia and NE Turkey. V. v. macroura Baird, 1852 — USA (Mountain States). V. v. montana Pearson, 1836 — Himalayas form China (Yunnan) to C Pakistan. V. v. mecator Merriam, 1900 — SW USA (California & Nevada). V. v. ochroxantha Ognev, 1926 — E Russian Turkestan, Aksai, Kirgizstan, Semirechie. V. v. palaestina Thomas, 1920 —Jordan and Lebanon. V.v. peculiosa Kishida, 1924 — Korea. V. v. pusilla Blyth, 1854 — NW India to Irak. V.v. regalis Merriam, 1900 — N Great Plains of Canada and USA. V. v. rubricosa Bangs, 1898 — E Canada. V.v. schrencki Kishida, 1924 — N Japan (Hokkaido) and NE Russia (Sakhalin). V. v. silacea G. S. Miller, 1907 — Iberian Peninsula. V.v. splendidissima Kishida, 1924 — E Russia (N & C Kurile Is). V. v. stepensis Brauner, 1914 — steppes of S Russia. V. v. tobolica Ognev, 1926 — Russia (lower basin of Ob River) V. v. tschiliensis Matschie, 1907 — NE China. Foxes of European origin were introduced into E USA and Canada in the 17" century, subsequently mixed with local subspecies. Also introduced to Australia in 1800s, and the Falkland Islands (Malvinas). in Canidae
Subspecies and Distribution. V. v. vulpes Linnaeus, 1758 — N Europe (Scandinavia). V. v. abietorum Merriam, 1900 — SW Canada (Alberta & British Columbia). V. v. aegyptiacus Sonnini, 1816 — Egypt, Israel, and Lybia. V. v. alascensis Merriam, 1900 — Alaska and NW Canada (NW Territories & Yukon). V. v. alpheraky: Satunin, 1906 — Kazakhstan. V. v. anatolica Thomas, 1920 — Turkey. V. v. arabica Thomas, 1902 — Arabian peninsula. V. v. atlantica Wagner, 1841 — Algeria (forested Atlas Mts). V. v. bangsi Merriam, 1900 — NE Canada (Labrador). V. v. barbara Shaw, 1800 — NW Africa (Barbary Coast). V. v. beringiana Middendorff, 1875 — NE Siberia (shore of Bering Strait). V. v. cascadensis Merriam, 1900 — NW USA (Cascade Mountains, Oregon & Washington). V. v. caucasica Dinnik, 1914 — SW Russia (Caucasus). V. v. crucigera Bechstein, 1789 — Europe through N & C Russia. V. v. daurica Ognev, 1931 — E Russia (Amur, Siberia & Transbaikalia). V.v. deletrix Bangs, 1898 — NE Canada (Newfoundland). V. v. dolichocrania Ognev, 1926 — SE Siberia (S Ussuri). V. v. flavescens Gray, 1843 — N Iran. V. v. fulva Desmarest, 1820 — E USA. V. v. griffith: Blyth, 1854 — Afghanistan and N Pakistan. V.v. harrimani Merriam, 1900 — Alaska (Kodiak I). V. v. hoole Swinhoe, 1870 — S China (Fujian to Sichuan). V. v. ichnusae G. S. Miller, 1907 — Corsica and Sardinia. V. v. induta G. S. Miller, 1907 — Cyprus. V. v. jakutensis Ognev, 1923 — E Siberia (S of Yakutsk). V. v. japonica Gray, 1868 — Japan. V. v. karagan Erxleben, 1777 — Mongolia, Kazakhstan, and Kirgizstan. V. v. kenaiensis Merriam, 1900 — Alaska (Kenai Peninsula). V. v. kurdistanica Satunin, 1906 — Armenia and NE Turkey. V. v. macroura Baird, 1852 — USA (Mountain States). V. v. montana Pearson, 1836 — Himalayas form China (Yunnan) to C Pakistan. V. v. mecator Merriam, 1900 — SW USA (California & Nevada). V. v. ochroxantha Ognev, 1926 — E Russian Turkestan, Aksai, Kirgizstan, Semirechie. V. v. palaestina Thomas, 1920 —Jordan and Lebanon. V.v. peculiosa Kishida, 1924 — Korea. V. v. pusilla Blyth, 1854 — NW India to Irak. V.v. regalis Merriam, 1900 — N Great Plains of Canada and USA. V. v. rubricosa Bangs, 1898 — E Canada. V.v. schrencki Kishida, 1924 — N Japan (Hokkaido) and NE Russia (Sakhalin). V. v. silacea G. S. Miller, 1907 — Iberian Peninsula. V.v. splendidissima Kishida, 1924 — E Russia (N & C Kurile Is). V. v. stepensis Brauner, 1914 — steppes of S Russia. V. v. tobolica Ognev, 1926 — Russia (lower basin of Ob River) V. v. tschiliensis Matschie, 1907 — NE China. Foxes of European origin were introduced into E USA and Canada in the 17" century, subsequently mixed with local subspecies. Also introduced to Australia in 1800s, and the Falkland Islands (Malvinas).
Distribution. Japan, mainly E Honshu and adjacent islands, as well as isolated populations in W Japan, including W Honshu (Hiwa Town, Kyoto City, and Kii Peninsula), Shikoku (Mt Ishizuchi, Mt Tsurugi, and Mt Ohtaki), and Shodoshima I; W limit of distribution on E Honshu is located across Ishikawa, Gifu, Nagano, and Shizuoka prefectures, where SmallJapanese Mole shows parapatric or mixed distribution with the Large Japanese Mole (M. wogura), a species distributed in W Japan. In Echigo Plain, Niigata Prefecture, the Small Japanese Mole is parapatric with the Echigo Mole (M. etigo). in Talpidae
Distribution. Japan, mainly E Honshu and adjacent islands, as well as isolated populations in W Japan, including W Honshu (Hiwa Town, Kyoto City, and Kii Peninsula), Shikoku (Mt Ishizuchi, Mt Tsurugi, and Mt Ohtaki), and Shodoshima I; W limit of distribution on E Honshu is located across Ishikawa, Gifu, Nagano, and Shizuoka prefectures, where SmallJapanese Mole shows parapatric or mixed distribution with the Large Japanese Mole (M. wogura), a species distributed in W Japan. In Echigo Plain, Niigata Prefecture, the Small Japanese Mole is parapatric with the Echigo Mole (M. etigo).
Distribution. WC core and SE peninsula of Sulawesi, including Mt Kanino, Mt Nokilalaki, Mt Lehio, Rano Rano, and Mamasa regions, Quarles Range, Mt Rantemario, and Mt Latimojong. Descriptive notes. er 155-242 mm, tail 138-190 mm, ear 23-29 mm, hind-foot 28-45 mm; weight 95-170 g. The Montane Hill Rat is the largest member of the B. fratrorum species group, with broad head, long rostrum, and robust body. Pelage is moderately long, soft, and lustrous, with shortish blackish guard hairs mixed throughout. Dorsum is brownish gray, speckled with buff that is a mix of dark gray underfur and overhairs with brown tips and buffy bands, being dark gray for the most part. Sides are paler grayish brown and fade into ventral pelage. Sides of muzzle are white. Venter is grayish white or dark grayish white, although some are grayish buff, with gray hairs and unpigmented tips or unpigmented altogether, respectively. Juveniles are duller and darker, with more grayish white underparts. Feet are long and slender, with white digits. Ears are large, covered in short unpigmented hair, rubbery, and gray and brown hues. Tail is 88-102% of head-body length and mainly bicolored, brownish gray to blackish gray dorsally and glossy white ventrally, with white tip most of the time. Scrotum is gray. Skull is large, with long and wide rostrum and narrow zygomatic plate. Fleas (e.g. Sigmactenus, Stivalius, Musserella, and Dasypsyllus), ticks (Rhipicephalus) pseudoscorpions (Magachernes and Chiridiochernes), and nematodes (Bunomystrongylus and Sibulura) have been recorded from the Montane Hill Rat. There are two pairs of inguinal mammae. Chromosomal complement is 2n = 42, FN = 60 (females) or FN = 61 (males). in Muridae
Distribution. WC core and SE peninsula of Sulawesi, including Mt Kanino, Mt Nokilalaki, Mt Lehio, Rano Rano, and Mamasa regions, Quarles Range, Mt Rantemario, and Mt Latimojong. Descriptive notes. er 155-242 mm, tail 138-190 mm, ear 23-29 mm, hind-foot 28-45 mm; weight 95-170 g. The Montane Hill Rat is the largest member of the B. fratrorum species group, with broad head, long rostrum, and robust body. Pelage is moderately long, soft, and lustrous, with shortish blackish guard hairs mixed throughout. Dorsum is brownish gray, speckled with buff that is a mix of dark gray underfur and overhairs with brown tips and buffy bands, being dark gray for the most part. Sides are paler grayish brown and fade into ventral pelage. Sides of muzzle are white. Venter is grayish white or dark grayish white, although some are grayish buff, with gray hairs and unpigmented tips or unpigmented altogether, respectively. Juveniles are duller and darker, with more grayish white underparts. Feet are long and slender, with white digits. Ears are large, covered in short unpigmented hair, rubbery, and gray and brown hues. Tail is 88-102% of head-body length and mainly bicolored, brownish gray to blackish gray dorsally and glossy white ventrally, with white tip most of the time. Scrotum is gray. Skull is large, with long and wide rostrum and narrow zygomatic plate. Fleas (e.g. Sigmactenus, Stivalius, Musserella, and Dasypsyllus), ticks (Rhipicephalus) pseudoscorpions (Magachernes and Chiridiochernes), and nematodes (Bunomystrongylus and Sibulura) have been recorded from the Montane Hill Rat. There are two pairs of inguinal mammae. Chromosomal complement is 2n = 42, FN = 60 (females) or FN = 61 (males).
Dataset and codes used in the manuscript entitled "A rainfall-tracking travel time distribution model to quantify mixing and storage release preference in a large shallow lake by two-year stable isotopic data"
<p>This contains the codes and dataset for the manuscript entitled "A rainfall-tracking travel time distribution model to quantify mixing and storage release preference in a large shallow lake by two-year stable isotopic data". Detailed information about the dataset is described in the Readme.txt file.</p>
Dataset to the manuscript titled "Mixing state, spatial distribution, sources and photochemical enhancement to sulfate formation of black carbon particles in the Arctic Ocean during summer"
Open the record for dataset details and reuse information.
Data from: Frequency and distribution of 152 genetic disease variants in over 100,000 mixed breed and purebred dogs
Open the record for dataset details and reuse information.
Frequency and Distribution of Mixed Falciparum-vivax Infections in French Guiana
ClinicalTrials.gov study NCT02903758. IPD Sharing: NO. Countries: 1. Publications: 0.
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