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opencc-by-4.0Jun 2021View details →

FIG. 1. — This concrete bridge replaced a in Pigs and ritual-hunting among the highland Tau-Buhid in Mounts Iglit-Baco natural park, Philippines

FIG. 1. — This concrete bridge replaced a hanging bridge as part of the State modernization plan for the Mounts Iglit-Baco Natural Park. For many Tau-Buhid, the concrete bridge represents a denial of their legal and customary rights within and over the extent of their lands, and is a threat to the survival of their way of life. Through this bridge, State surveillance and control of highland activities intensified. Photo credits: C. A. Rosales.

opencc-by-4.0Jun 2021View details →

FIG. 7 in Pigs and ritual-hunting among the highland Tau-Buhid in Mounts Iglit-Baco natural park, Philippines

FIG. 7. — Fufuama (grandfather, elder) Butodaol, leader of the highland TauBuhid. Photo credits: C. A. Rosales.

Fig. 5 in Preliminary observations of macrobenthic invertebrates and megafauna communities in the upper mesophotic coral ecosystems in Apo Reef Natural Park, Philippines

Fig. 5. Barplots represent the total species richness across the depths (A) and reef types (B). C and E show the abundance of macrobenthic invertebrates and megafauna, respectively, with their corresponding trophic groups across depths. D and F show the abundance of macrobenthic invertebrates and megafauna, respectively, with their corresponding trophic groups across reef types.

Fig. 3 in Preliminary observations of macrobenthic invertebrates and megafauna communities in the upper mesophotic coral ecosystems in Apo Reef Natural Park, Philippines

Fig. 3. Macrobenthic invertebrate species in Apo Reef Natural Park. A, Holothuria atra; B, Holothuria fuscogilva; C, Thelenota anax; D, Thelenotarubra lineata; E, Thromidia catalai; F, Tridacna sp.; G, Xetospongia sp.

Fig. 2 in Preliminary observations of macrobenthic invertebrates and megafauna communities in the upper mesophotic coral ecosystems in Apo Reef Natural Park, Philippines

Fig. 2. Reef fish and marine reptile megafaunal species in Apo Reef Natural Park. A, Eretmochelys imbricata; B, Bolbometopon muricatum; C, Balistoides viridescens; D, Cheilinus undulatus; E, Caranx melampygus; F, Cephalopholis argus; G, Macolor niger; H, Sphyraena qenie; I, Triaenodon obesus.

Fig. 1 in Preliminary observations of macrobenthic invertebrates and megafauna communities in the upper mesophotic coral ecosystems in Apo Reef Natural Park, Philippines

Fig. 1. Map showing the location of Apo Reef Natural Park in the Philippines, as well as, the study sites that were surveyed in March 2016.

Fig. 4 in Preliminary observations of macrobenthic invertebrates and megafauna communities in the upper mesophotic coral ecosystems in Apo Reef Natural Park, Philippines

Fig. 4. Results of the non-metric multidimensional scaling (nMDS) across depths (A) and reef types (B). Analysis of similarity (ANOSIM) results along with the corresponding p values are included in the plots (A and B). Vectors showing the influence (direction and magnitude) of the different benthic cover on the species composition (C).

opencc-by-4.0Mar 2023View details →

Рис. 8–13. ΔанΑшафты Южного УраΛа (8–11) и Русской равнины (12–13). 8 – разнотравная степь у поΑножия горы ВербΛюжка, местообитание Cionus rossicus; 9 – ксерофитные Λуга в пойме реки УраΛ вбΛизи горы ВербΛюжка, местообитание Cionus rossicus; 10 – южные степи в районе КзыΛаΑырского карстового поΛя, местообитание Cionus gebleri; 11 – степи низкогорий Южного УраΛа бΛиз с. КиΑрясово, местообитание Smicronyx albopictus; 12 – КаменноброΑские меΛовые горы на юго-запаΑе ПривоΛжской возвышенности, местообитание Mecinus janthiniformis, Smicronyx robustus и S. albopictus; 13 – меΛовой останец КобыΛья ГоΛова в прироΑном парке «Àонской», местообитание Mecinus janthiniformis. Figs 8–13. Landscapes of the Southern Urals (8–11) and the Russian Plain (12–13). 8 – forb steppe at the down of Verblyuzhka Mt., habitat of Cionus rossicus; 9 – xerophytic meadows in the floodplain of the Ural River near Verblyuzhka Mt., habitat of Cionus rossicus; 10 – southern steppes in the Kzyladyr karst area, habitat of Cionus gebleri; 11 – steppes of the low mountains of the Southern Urals near Kidryasovo village, habitat of Smicronyx albopictus; 12 – Kamennobrodsky chalk mountains in the southwest of the Volga Upland, habitat of Mecinus janthiniformis, Smicronyx robustus, and S. albopictus; 13 – Cretaceous outlier Kobyl'ya Golova in the Donskoy Nature Park, habitat of Mecinus janthiniformis. in Interesting records of weevils (Coleoptera: Curculionidae: Curculioninae) in the steppe zone of the European part of Russia and the Urals

Рис. 8–13. ΔанΑшафты Южного УраΛа (8–11) и Русской равнины (12–13). 8 – разнотравная степь у поΑножия горы ВербΛюжка, местообитание Cionus rossicus; 9 – ксерофитные Λуга в пойме реки УраΛ вбΛизи горы ВербΛюжка, местообитание Cionus rossicus; 10 – южные степи в районе КзыΛаΑырского карстового поΛя, местообитание Cionus gebleri; 11 – степи низкогорий Южного УраΛа бΛиз с. КиΑрясово, местообитание Smicronyx albopictus; 12 – КаменноброΑские меΛовые горы на юго-запаΑе ПривоΛжской возвышенности, местообитание Mecinus janthiniformis, Smicronyx robustus и S. albopictus; 13 – меΛовой останец КобыΛья ГоΛова в прироΑном парке «Àонской», местообитание Mecinus janthiniformis. Figs 8–13. Landscapes of the Southern Urals (8–11) and the Russian Plain (12–13). 8 – forb steppe at the down of Verblyuzhka Mt., habitat of Cionus rossicus; 9 – xerophytic meadows in the floodplain of the Ural River near Verblyuzhka Mt., habitat of Cionus rossicus; 10 – southern steppes in the Kzyladyr karst area, habitat of Cionus gebleri; 11 – steppes of the low mountains of the Southern Urals near Kidryasovo village, habitat of Smicronyx albopictus; 12 – Kamennobrodsky chalk mountains in the southwest of the Volga Upland, habitat of Mecinus janthiniformis, Smicronyx robustus, and S. albopictus; 13 – Cretaceous outlier Kobyl'ya Golova in the Donskoy Nature Park, habitat of Mecinus janthiniformis.

Fig. 4 in Orthopteran diversity and distribution in the Monviso Natural Park (Western Italian Alps) (Orthoptera)

Fig. 4 – Plot representing the species-sample rarefaction curve, calculat- ed using the 2019-2020 surveys data (1200 records in 395 survey points, 49 species). The grey area identifies the 95% confidence interval.

Fig. 3 in Orthopteran diversity and distribution in the Monviso Natural Park (Western Italian Alps) (Orthoptera)

Fig. 3 – Map of the study area reporting the number of survey points in each 1x1 km cell (N = 423; red circles). The unexplored cells are identified with a "X", while unfilled circles indicate cells where no surveys were carried out, due to the absence of orthoptera.

Fig. 2 in Orthopteran diversity and distribution in the Monviso Natural Park (Western Italian Alps) (Orthoptera)

Fig. 2 – Map of the study area showing the position of the 28 additional survey points (90 records) reported in literature or in the considered databases (MB = M. Bonifacino's archive; RS = R. Sindaco's archive; PRND = Piemonte Region Naturalistic Database).

Fig. 6 in Orthopteran diversity and distribution in the Monviso Natural Park (Western Italian Alps) (Orthoptera)

Fig. 6 – Barplots showing the distribution of survey points (grey bars) and observed species richness (black bars) along A, the altitudinal gradient within the study area, and B, in each month during the research period.

Fig. 1 in Orthopteran diversity and distribution in the Monviso Natural Park (Western Italian Alps) (Orthoptera)

Fig. 1 – Map showing the geographical position of the study area (Monviso massif, Cottian Alps, Piedmont, Italy). The Monviso Natural Park (yellow line, pale green area) and the SAC/SPA IT1160058 "Gruppo del Monviso e Bosco dell'Alevé" (red line) borders are reported, together with the 1x1 km lattice (UTM grid, zone 32 N) used as spatial reference during this research (in black). Red dots identify the 395 survey points (1200 records) investigated by the author in 2019-2020.

opencc-by-4.0Dec 2019View details →

"The sound comes from a meadow in the Sierra Nevada Mountains in California. The meadow is at an elevation of 2400 meters near a mountain named Olancha Peak, which is 3700 meters in altitude. Ihave a group of friends with which Ibackpack (trek) into the mountains. Our goal was to spend some time in the mountains and hike to the top of Olancha Peak (…) By the time we reached the meadow, we were in a forest and there was still snow on the ground in some places. We took the trip in June of 2006. The Sierra Nevada Mountains are a large mountain range. Much of the range is protected by national parks or preserved areas we call 'wilderness areas' (…) Ihave been backpacking for nearly 40 years and Iwill hopefully continue with this challenging activity for 40 years more! Many of my friends are much younger than Iam and it gives me much satisfaction to be able to have as much or more stamina for this activity than they have! When we are on these trips, we hike up peaks, catch fish, drink some whiskey around campfires and enjoy our time in the beautiful solitude. My memories of this trip were of the steep, hot hike from the desert to the cool meadow; the overall beauty of the nature, the absolute solitude of our campsite near the meadow; the strenuous hike to the top of Olancha Peak; the camaraderie of my friends; and, of course the sound of the frogs in the meadow. The frog sounds were astounding to me and Iwould listen in awe of the creature's instinctual desire to reproduce and continue the existence of their kind. Surely there were different species in the meadow for some of the frog sounds were different than others. The sounds only occurred after the Sun went down for the evening. Istood next to the creek in the meadow and recorded the sounds using my digital camera." [Peter/plentz1960]16 in Collecting Sounds. Online Sharing of Field Recordings as Cultural Practice

"The sound comes from a meadow in the Sierra Nevada Mountains in California. The meadow is at an elevation of 2400 meters near a mountain named Olancha Peak, which is 3700 meters in altitude. Ihave a group of friends with which Ibackpack (trek) into the mountains. Our goal was to spend some time in the mountains and hike to the top of Olancha Peak (…) By the time we reached the meadow, we were in a forest and there was still snow on the ground in some places. We took the trip in June of 2006. The Sierra Nevada Mountains are a large mountain range. Much of the range is protected by national parks or preserved areas we call 'wilderness areas' (…) Ihave been backpacking for nearly 40 years and Iwill hopefully continue with this challenging activity for 40 years more! Many of my friends are much younger than Iam and it gives me much satisfaction to be able to have as much or more stamina for this activity than they have! When we are on these trips, we hike up peaks, catch fish, drink some whiskey around campfires and enjoy our time in the beautiful solitude. My memories of this trip were of the steep, hot hike from the desert to the cool meadow; the overall beauty of the nature, the absolute solitude of our campsite near the meadow; the strenuous hike to the top of Olancha Peak; the camaraderie of my friends; and, of course the sound of the frogs in the meadow. The frog sounds were astounding to me and Iwould listen in awe of the creature's instinctual desire to reproduce and continue the existence of their kind. Surely there were different species in the meadow for some of the frog sounds were different than others. The sounds only occurred after the Sun went down for the evening. Istood next to the creek in the meadow and recorded the sounds using my digital camera." [Peter/plentz1960]16

opencc-by-4.0Oct 2023View details →

Training set of microscopy images for Park et al. Nature Methods 2023

All data for key-point tracking:keypoint-tracking-data-*.h5Videos illustrating key-point tracking:keypoint-tracking-videos.zipSample data for 3D volume tracking and videos:volumetric-tracking-data-and-videos.zip

opencc-by-4.0Apr 2009View details →

Figure 2 in Roncus elbulli (Arachnida, Pseudoscorpiones), a new species from Cap de Creus Nature Park (Catalonia, Spain), with a key to the Spanish species of the genus Roncus

Figure 2. Habitus of Roncus elbulli sp. n. (Cap de Creus, October 2002).

opencc-by-4.0Apr 2009View details →

Figure 1 in Roncus elbulli (Arachnida, Pseudoscorpiones), a new species from Cap de Creus Nature Park (Catalonia, Spain), with a key to the Spanish species of the genus Roncus

Figure 1. Map showing the bay slopes "calas" where Roncus elbulli sp. n. is found.

opencc-by-nc-4.0Jul 2020View details →

Figure 1 in Andean bear (Tremarctos ornatus) population density and relative abundance at the buffer zone of the Chingaza National Natural Park, cordillera oriental of the colombian andes

Figure 1. Natural covers map showing camera traps distribution at 9 grids throughout the study area.

opencc-by-4.0Mar 2024View details →

Spectral library of plant species from Montesinho Natural Park in Portugal

The database contains the average spectra for leaves of each species, collected in different grids. Additionally, there is at least one photographic record for each species and the calculation of different Vegetation Indices (VIs), namely: Normalized Difference Vegetation Index (NDVI), Simple Ratio (SR), Renormalized Difference Vegetation Index (RDVI), Greenness Index (GI), and Structure Insensitive Pigment Index (SIPI). A detailed description regarding the database, its content, and the measurement instrument can be found in the database report and in a data paper (In Prep). It showcases some of the most representative and relevant vascular plant species within a conservation area in Portugal - the Montesinho Natural Park (MNP), namely: Alnus glutinosa (L.) Gaertn, Castanea sativa Mill., Cistus ladanifer L., Crataegus monogyna Jacq., Frangula alnus Mill., Fraxinus angustifolia Vahl, Quercus pyrenaica Willd., Quercus rotundifolia Lam., Trifolium repens L., Arbutus unedo L. Dactylis glomerata L., Genista falcata Brot., Cytisus multiflorus (L*Hér.) Sweet, Erica arborea L., and Acacia dealbata Link. Samples were collected in situ on June 21st and 22nd, 2023.