Find research datasets worth reusing

opencc-by-4.0Dec 2019View details →

Datasets for the publication "Simulation of snow management in Alpine ski resorts using three different snow models"

Snow model simulation results used for the paper "Simulation of snow management in Alpine ski resorts using three different snow models". The following results are available for each of the nine ski resorts: <ul> <li><resort>_swe_<date>.tif or <resort>_swe.geojson: Spatially distributed SWE outputs for 2016-12-24 and 2017-12-24 in GeoJSON (for the two French resorts) or GeoTIFF (for all other resorts) format. Unit: kg m-2</li> <li><resort>_point_depth.csv, <resort>_point_swe.csv: Time series of snow depth (in m) and SWE (in kg m-2) for the respective points of interest. The column names correspond to the snow management configurations as shown in Fig. 5 of the paper.</li> </ul>

opencc-by-4.0Dec 2015View details →

Figure 3 in Biology and management of the masked chafer Cyclocephala disticcta Burmeister &Melolonthidae, Dynastinae, Cyclocephalini)

Figure 3. Adult Cyclocephala disticcta bred in captivity. A, Newly hatched male; B, Male one day after hatching; C, Liquid*releasing behavior. Adult mean size: 10 mm.

opencc-by-4.0Dec 2015View details →

Figure 2 in Biology and management of the masked chafer Cyclocephala disticcta Burmeister &Melolonthidae, Dynastinae, Cyclocephalini)

Figure 2. Larval stage of Cyclocephala disticcta bred in captivity. A, Larva of the 2nd instar defecating &mean size: 1.3 mm); B, Cephalic capsule of the 1st, 2nd and 3rd instars, respec* tively; C, Transition between the 3rd instar &below) and pre*pupa &above).

Fig. 9. Core ARD 3 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 9. Core ARD 3 selected percentage testate amoebae diagram, data are presented as percentages of the total testates in each level. The diagram has been subdivided into zones to better aid interpretation. Note that in the older literature (including all the more accessible identification guides) Archerella flavum is refered to as Amphitrema flavum.

Fig. 5. Testate amoebae from the top 20 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 5. Testate amoebae from the top 20 cm of Holcroft Moss, data are presented as percentages of the total testates in each level. The diagram has been subdivided into zones (HM I – HMIV) to better aid interpretation. The zones were defined by a combination of simple inspection and multivariate analysis.

Fig. 8. Core ARD 2 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 8. Core ARD 2 selected percentage testate amoebae diagram, data are presented as percentages of the total testates in each level. The diagram has been subdivided into zones to better aid interpretation. Note that in the older literature (including all the more accessible identification guides) Archerella flavum is refered to as Amphitrema flavum.

Fig. 7. Core ARD 1 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 7. Core ARD 1 selected percentage testate amoebae diagram, data are presented as percentages of the total testates in each level. The diagram has been subdivided into zones to better aid interpretation. Note that in the older literature (including all the more accessible identification guides) Archerella flavum is refered to as Amphitrema flavum and Padaungiolla lageniformis is called Nebela lageniformis.

Figure 9 in Human-wildlife conflict as a barrier to large carnivore management and conservation in Turkey

Figure 9. Responses by occupation for the question "Does the wild animal you see harm you?" as part of a human opinion survey conducted in 2010 and 2014 in villages surrounding the Sarıkamış-Allahuekber Mountains National Park in eastern Turkey. Results are pooled across years.

Figure 12 in Human-wildlife conflict as a barrier to large carnivore management and conservation in Turkey

Figure 12. Previous knowledge of wildlife ecotourism and desire to participate in future opportunities of survey respondents to a human opinion survey conducted in 2010 and 2014 in villages surrounding the Sarıkamış-Allahuekber Mountains National Park in eastern Turkey. Results are pooled across the two survey years.

Figure 6 in Human-wildlife conflict as a barrier to large carnivore management and conservation in Turkey

Figure 6. Responses by survey year for the question "Does the wild animal you see harm you?" as part of a human opinion survey conducted in 2006, 2010, and 2014 in villages surrounding the Sarıkamış-Allahuekber Mountains National Park in eastern Turkey.

Figure 7 in Human-wildlife conflict as a barrier to large carnivore management and conservation in Turkey

Figure 7. Property damage from wildlife experienced by survey respondents to a human opinion survey conducted in 2006, 2010, and 2014 in villages surrounding the Sarıkamış-Allahuekber Mountains National Park in eastern Turkey. Results are pooled across years.

Figure 2 in Density, diversity, and seasonal fluctuations in soil Collembola in three differently managed ecosystems in North Khorasan, Iran

Figure 2. Map of Iran and location of the study area (Golil-Sarany, the protected rangeland) along with the IRS-P6 LISS III satellite image of the area.

Figure 1 in Density, diversity, and seasonal fluctuations in soil Collembola in three differently managed ecosystems in North Khorasan, Iran

Figure 1. Map of Iran. a) Map of Iranian provinces, b) Study area indicated by arrow (North Khorasan province).

Figure 8 in Density, diversity, and seasonal fluctuations in soil Collembola in three differently managed ecosystems in North Khorasan, Iran

Figure 8. Density of dominant Ceratophysella gibbosa in different ecosystems over the study period (2018–2019).

Figure 3 in Density, diversity, and seasonal fluctuations in soil Collembola in three differently managed ecosystems in North Khorasan, Iran

Figure 3. Climatogram (monthly measurements of temperature and precipitation) of the study area, Shirvan, based on the data obtained from the Meteorological Station of Shirvan over the period 2004–2014.

Figure 5 in Density, diversity, and seasonal fluctuations in soil Collembola in three differently managed ecosystems in North Khorasan, Iran

Figure 5. Nonmetric multidimensional scaling (nMDS) plot. Resemblance pattern of soil Collembolan fauna in three ecosystems, using total density of each taxon. Groups are delineated according to the results of the cluster analysis.

opencc-by-4.0Jul 2024View details →

Figure 2 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices

Figure 2. Trend of sea turtle nesting in the past 40 years at APNP: (A) L.olivacea, (B) C. mydas, (C) E. imbricata, and (D) D. coriacea.

opencc-by-4.0Jul 2024View details →

Figure 1 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices

Figure 1. Study location in Alas Purwo National Park's Pancur-Cungur Coast with six hypothetical stations (dot: sector benchmark point).

opencc-by-4.0Jul 2024View details →

Figure 4 in Spatial and temporal nesting pattern of Sea Turtles in Alas Purwo National Park, and its implications for conservation management practices

Figure 4. Number of four sea turtles nesting in each month during survey period: (A) L.olivacea, (B) C. mydas, (C) E. imbricata, and (D) D. coriacea.