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13 results for “Japan Basin”
Fig. 1. A in Distribution of Fish Parasites Argulus japonicus and Argulus coregoni (Crustacea: Branchiura: Argulidae) in the Lake Biwa Basin, Central Japan
Fig. 1. A map of Shiga Prefecture, central Japan, to show the distribution of Argulus japonicus (closed circles, in Lake Biwa; closed triangle, in Chirinsan-no-ike Pond) and A. coregoni (open circles) in the Lake Biwa Basin. Only large rivers are shown. Dashed lines indicate the borders of Shiga and neighboring prefectures. 1, Katayama; 2, Onoe; 3, near the mouth of the Uso River; 4, off Omi-maiko; 5, Wani-Imajuku; 6, Akanoi; 7, Shina; 8, Hiei-tsuji; 9, Chirinsan-no-ike Pond; 10, Otsu; 11, Harihata River; 12, lower Ado River; 13, Kawachidani Stream; 14, upper Ane River; 15, Oike River; 16, Kanzaki River. See Tables 1 and 2 for detailed information on the collection localities of A. japonicus and A. coregoni, respectively.
Fig. 2 in Pseudorhadinorhynchus samegaiensis (Acanthocephala: Echinorhynchida: Illiosentidae) Uses the Amphipod Jesogammarus (Annanogammarus) fluvialis as an Intermediate Host in a Stream of the Lake Biwa Basin, Central Japan
Fig. 2. Developmental stages of Pseudorhadinorhynchus samegaiensis. A, Male acanthella; B, early male cystacanth with part of proboscis and copulatory bursa everted, same individual as "c" in Fig. 1B; C, early female cystacanth; D, fully developed male cystacanth with everted proboscis; E, fully developed female cystacanth with everted proboscis; F, everted proboscis of fully developed female cystacanth (E). Scale bars: A, 300 µm; B–E, 500 µm; F, 200 µm.
Fig. 1. Acanthocephalus minor Yamaguti, 1935 in Rediscovery of a Fish Acanthocephalan, Acanthocephalus minor (Echinorhynchida: Echinorhynchidae), in the Lake Biwa Basin, Central Japan, with a Review of the Fish Acanthocephalan Fauna of the Basin
Fig. 1. Acanthocephalus minor Yamaguti, 1935, NSMT–As 4293, from rectum of Odontobutis obscura (Temminck and Schlegel, 1845). A, Entire body of male; B, proboscis of female. Scale bars: A, 1 mm; B, 100 µm.
Groundwater level change data set and SAR analysis data set from the end of 2016 to the end of 2020 in the Osaka Plain and Kyoto Basin, Japan
<p>The .dat file contains data on groundwater level changes. Groundwater level data is hourly, and each line contains data for one day (24 hours). The name of the .dat files consists of the name of the groundwater level station and the observation period. Datasets that include raw in the name contain the respective date in the first column.</p> <p>Source: Water information System, Ministry of Land, Infrastructure, Transport and Tourism, 2017-2020. Groundwater level search results, http://www1.river.go.jp/ (accessed on 20 October 2021) [Translated from Japanese.] (In Japanese).</p> <p>SLC data for InSAR analysis can be obtained by running the .py file in python. python files are provided to obtain SLC data by two orbits, Ascending and Descending, respectively.</p> <p>Source: European Space Agency (ESA), https://search.asf.alaska.edu/#/</p>
Current meter measurements on the southern rim slope of the Yamato Basin in the Japan Sea
<p>This dataset contains measurements from moored current meters and hydrographic observations in the southern Japan Sea. </p> <p>These are for the publication of the manuscript entitled "Local topographic Rossby modes observed in the abyssal Japan Sea" by Senjyu, T., which will be submitted to Journal of Physical Oceanography. </p>
РИС. 8. Примеры проблем с иЗображением при работе на СЭМ. А, В. Засветка раЗличных частей раковин глохидиев (А. Anodonta anatina (=Colletopterum), оЗ. Красное, ХакасиЯ. В. Inversiunio reinianus, оЗ. Бива, о-в Хонсю, ЯпониЯ). C. РаЗнаЯ скорость сканированиЯ (слева – очень быстраЯ, справа – медленнаЯ) наружной поверхности глохидиЯ (Anodonta cygnea, р. Ялма, МосковскаЯ обл.). D. Артефакты в виде гориЗонтальных полос вследствие накоплениЯ отрицательного ЗарЯда при недостаточном напылении внутренней поверхности глохидиЯ (Nodularia douglasiae, ПетровскаЯ протока, бассейн р. Амур, Хабаровский кр.). МасШтаб 50 мкм (А, В), 2 мкм (С), 5 мкм (D). Микроскопы Zeiss EVO 40 (А, С, D), Zeiss MERLIN (В), напыление углеродом (А, С), хромом (В, D). FIG. 8. Illustration of different problems with SEM images. A, B. Overall illumination of some glochidia shells parts (A. Anodonta anatina (= Colletopterum), Krasnoe Lake, Khakassia. B. Inversiunio reinianus, Biwa Lake, Honshu Island, Japan). C. Different scanning speed (faster on the left and slower on the right) of the exterior glochidia valve (Anodonta cygnea, Yalma River, Moscow Oblast). D. Artifacts as horizontal stripes because of additional accumulation of a negative charge due to insufficient coating of the interior glochidia valve (Nodularia douglasiae, Petrovskaya channel, Amur River basin, Khabarovsk Krai). Scale bars 50 μm (A, B), 2 μm (C), 5 μm (D). Zeiss EVO 40 (A, C, D) and Zeiss MERLIN (B) microscopes, sputter coating with carbon (A, C) and chromium (B, D). in Методика подготовки раковин глохидиев (Bivalvia, Unionidae) длЯ работы на сканируюЩем Электронном микроскопе
РИС. 8. Примеры проблем с иЗображением при работе на СЭМ. А, В. Засветка раЗличных частей раковин глохидиев (А. Anodonta anatina (=Colletopterum), оЗ. Красное, ХакасиЯ. В. Inversiunio reinianus, оЗ. Бива, о-в Хонсю, ЯпониЯ). C. РаЗнаЯ скорость сканированиЯ (слева – очень быстраЯ, справа – медленнаЯ) наружной поверхности глохидиЯ (Anodonta cygnea, р. Ялма, МосковскаЯ обл.). D. Артефакты в виде гориЗонтальных полос вследствие накоплениЯ отрицательного ЗарЯда при недостаточном напылении внутренней поверхности глохидиЯ (Nodularia douglasiae, ПетровскаЯ протока, бассейн р. Амур, Хабаровский кр.). МасШтаб 50 мкм (А, В), 2 мкм (С), 5 мкм (D). Микроскопы Zeiss EVO 40 (А, С, D), Zeiss MERLIN (В), напыление углеродом (А, С), хромом (В, D). FIG. 8. Illustration of different problems with SEM images. A, B. Overall illumination of some glochidia shells parts (A. Anodonta anatina (= Colletopterum), Krasnoe Lake, Khakassia. B. Inversiunio reinianus, Biwa Lake, Honshu Island, Japan). C. Different scanning speed (faster on the left and slower on the right) of the exterior glochidia valve (Anodonta cygnea, Yalma River, Moscow Oblast). D. Artifacts as horizontal stripes because of additional accumulation of a negative charge due to insufficient coating of the interior glochidia valve (Nodularia douglasiae, Petrovskaya channel, Amur River basin, Khabarovsk Krai). Scale bars 50 μm (A, B), 2 μm (C), 5 μm (D). Zeiss EVO 40 (A, C, D) and Zeiss MERLIN (B) microscopes, sputter coating with carbon (A, C) and chromium (B, D).
Data from: A basin-scale application of environmental DNA assessment for rare endemic species and closely related exotic species in rivers: a case study of giant salamanders in Japan
1. To prevent the invasion of exotic species causing a decline in an endangered endemic species, it is important to determine the distribution of both species at an early stage, when the density of the exotic species is still low, and to manage the invasion immediately. However, distinguishing between closely related species is difficult because they share similar characteristics. 2. The identification of DNA fragments sampled from a body of water (environmental DNA) has become a popular technique for rapidly determining the distribution of a target species. In this study, we analysed environmental DNA in water samples from 37 sites across the Katsura River basin in Japan. We used TaqMan real-time PCR to distinguish the Japanese giant salamander Andrias japonicus from the closely related Chinese giant salamander Andrias davidianus, which is known to invade Japanese rivers and hybridize with the Japanese species. 3. In environmental samples, we detected mtDNA of the endemic species at 25 sites and mtDNA of the exotic species at nine sites. The DNA detection sites were concentrated in the upstream region. The exotic species DNA was found beyond the limits of an earlier capturing survey. 4. Synthesis and applications. Using environmental DNA to monitor the two salamander species requires less time and effort than traditional surveys, so a wide-ranging survey can be conducted rapidly. Our results showed that performing three environmental DNA surveys for each site between autumn and winter is desirable for giant salamanders. Further collection of environmental DNA, in combination with conventional population surveys, will provide valuable information that can help protect rare endemic species in a variety of aquatic ecosystems and can help monitor the invasion of exotic species.
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. 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).
Teleseismic waveforms of OBS in Japan Basin
<p>The dataset includes the original teleseismic S waveforms and surface waveforms used in Receiver function and Rayleigh wave H/V ratio calculations, which are presented in the manuscript "Layered evolution of the oceanic lithosphere beneath the Japan Basin, the Sea of Japan" submitted to Journal of Geophysical Research - Solid Earth.</p> <p>Contact information: Sanxi Ai (aisanxi@cug.edu.cn) & Takeshi Akuhara (akuhara@eri.u-tokyo.ac.jp)</p>
Data from: A basin-scale application of environmental DNA assessment for rare endemic species and closely related exotic species in rivers: a case study of giant salamanders in Japan
Open the record for dataset details and reuse information.
Fig. 1 in Pseudorhadinorhynchus samegaiensis (Acanthocephala: Echinorhynchida: Illiosentidae) Uses the Amphipod Jesogammarus (Annanogammarus) fluvialis as an Intermediate Host in a Stream of the Lake Biwa Basin, Central Japan
Fig. 1. Jesogammarus (Annanogammarus) fluvialis infected with two fully developed cystacanths (a, b) and one early cystacanth (c) of Pseudorhadinorhynchus samegaiensis. A, Lateral view of amphipod harboring three cystacanths in hemocoel; B, three cystacanths dissected free from amphipod. Note faint orange spots (a, b) in amphipod's hemocoel (A) and faint orange body surface of cystacanths (B). Scale bars: A, 2 mm; B, 1 mm.
Rotated Transtensional Basins Formed During Back-arc Spreading in Japan: Simultaneous Rapid Tectonic Rotation and Basin Subsidence
<p>This is a supplemenaty table and data for manuscript submitted to Tectonics.</p>
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
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The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
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