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1,989 results for “Fires”
Fig. 8 in Action Plan For The Fire-Bellied Toad Bombina Bombina In Latvia: Assessment Of The Implementation For Ten Years, Releasing From Aquaculture And Restoration Of Habitats In 2006-2016
Fig. 8. Fitted linear model of the relationship between Actions' implementation before and after BAP.
Fig. 7 in Action Plan For The Fire-Bellied Toad Bombina Bombina In Latvia: Assessment Of The Implementation For Ten Years, Releasing From Aquaculture And Restoration Of Habitats In 2006-2016
Fig. 7. Box-and-Whicker plots for Species Conservation and Habitats Conservation Sub-actions' implementation in points before and after BAP.
FIGURE 3. A plaster and burlap cradle containing MOR 1184 in Non-traditional applications of fire in fossil preparation
FIGURE 3. A plaster and burlap cradle containing MOR 1184 being burned away from the entrapped fossil.
FIGURE 1. A. A in Non-traditional applications of fire in fossil preparation
FIGURE 1. A. A fossil in the field subsequent to flipping the jacket shows the extent of root growth across the surface of the bone, and infiltrating the bone and rock (MWC 9874). B. The same specimen, with the root system highlighted in white to better illustrate the pervasiveness of the root network.
Figure 2 in Fire effects on Atlantic Forest sites from a composition, structure and functional perspective
Figure 2. Average of species richness (A), basal area (B), Shannon index (C), tree density (D), CWM Height (E), CWM Leaf length (F), CWM wood density (G), CWM Leaf deciduousness (H), CWM dispersal mode (I), CWM shade tolerance (J) for tree species inventoried in burned and unburned sites in Paraíba do Sul river basin, Southeast Atlantic Forest biome, Brazil.Same letters represent no statistical difference.
Figure 3 in Avifauna of the Adelbert Mountains, New Guinea: why is Fire-maned Bowerbird Sericulus bakeri the mountains' only endemic bird species?
Figure 3. Terrain map of north-east New Guinea. Areas above 500 m are coloured grey; areas between 300 and 500 m blue; and areas below 300 m green. 1 = the Gogol River valley, between the Adelbert Mts. to the north and the Finisterre Mts. of the Huon Peninsula to the south. 2 = the Ramu River valley, between the Adelberts to the north-east and the Central Range to the south-west. 3 = the upper Ramu River valley and its headwaters, between the Finisterre Mts. of the Huon Peninsula to the north and the Central Range to the south. 4 = the Sepik River basin, between the Adelbert Mts. to the east and Prince Alexander Mts. of the North Coastal Range to the west. Map kindly produced by Iain Woxvold.
Figure 2 in Avifauna of the Adelbert Mountains, New Guinea: why is Fire-maned Bowerbird Sericulus bakeri the mountains' only endemic bird species?
Figure 2. Presence and absence of Sericulus bowerbirdsȱonȱNewȱGuinea'sȱnorthernȱwatershed,ȱmodifiedȱfromȱ Diamondȱ(1969).ȱEachȱfilledȱdotȱrepresentsȱrecordsȱbyȱoneȱobserver.ȱThereȱareȱonlyȱsevenȱdocumentedȱareasȱ of occurrence of the allospecies Masked Bowerbird S. aureus, numbered from west to east, with observer names in parentheses: 1 = Tamrau Mts. (E. T. Gilliard and B. M. Beehler) and Arfak Mts. (many observers) of the Vogelkop. 2 = Wandammen Mts. (E. Mayr). 3 = Weyland Mts. (F. Shaw-Mayer). 4 = Bernhard Camp (A. Rand). 5 = Foja Mts. (B. M. Beehler and J. Diamond). 6 = Mt. Nibo (J. Diamond). 7 = Mt. Turu (J. Diamond). The asterisk depicts the range of the allospecies Fire-maned Bowerbird S. bakeri in the Adelberts. X = areas surveyedȱintensivelyȱwithoutȱfindingȱanyȱSericulus.? = an undocumented report of S. aureus from the Jimi River.ȱExceptȱforȱtheȱlatter,ȱS. aureus is known mainly from outlying ranges (locations 1, 2, 5, 6 and 7). There are only two documented localities for it in the Central Range (3–4), and there is a large gap between the easternmost record of S. aureus (7) and the range of S. bakeri. The remaining Sericulus allospecies in New Guinea is Flame Bowerbird S. ardens of the southern watershed.
Figure 1 in Avifauna of the Adelbert Mountains, New Guinea: why is Fire-maned Bowerbird Sericulus bakeri the mountains' only endemic bird species?
Figure 1. New Guinea's principal mountain ranges: the Central Range forming New Guinea's backbone; and the ten outlying ranges along the north and north-west coasts, from Huon and Adelbert in the east, to Fakfak and Kumawa in the west.
Sensitivity of fire weather indices, fuel sticks and satellite observations to fuel moisture content in Central European forests - Data
<p>This data repository contains datasets for destructively measured fuels of different types (FMC_insitu), meteorological data including 10-hour fuel stick measurements (FWS_30min) and calculated fire weather index components (FWS_FWI_24h) for four different sites in the Tharandt forest and Saxon Switzerland National Park in the Free State of Saxony (Germany) during the years 2022 (only DE-Tha) and 2023 (all four sites).</p> <p>The provided folders contain .csv files for each study site. Meteorological data in 30min for DE-Tha can be derived from the ICOS data portal (https://data.icos-cp.eu/portal/). For the remaining three sites (DE-BLB, DE-BWB, DE-SHW), past and recent data can be viewed via EMS Brno (e.g., http://www.emsbrno.cz/p.axd/en/Beech__Landberg.TU__DRESDEN.html). Upon request, the authors can share the data. </p> <p><strong>FMC_insitu</strong>: Destructively sampled fuel moisture content of different fuel types.</p> <p><strong>FWS_30min</strong>: Original measurements from the fire weather stations in 30 min time steps</p> <p><strong>FWS_FWI_24h</strong>: Measurements from fire weather stations in 24h time steps and the calculated fire weather index and its components. As requested for calculation of the FWI, meteorological variables are used at 13:00 (UTC), while PREC and PBC are the 24h sum prior to 13:00. </p> <p><strong>readme.txt</strong>: Description of repository content and the variables provided within the .csv files.</p> <p><strong>stations.csv</strong>: Contains the coordinates and a short description of the study sites. </p>
Fig. 1 in The red imported fire ant (Hymenoptera: Formicidae) in the West Indies: distribution of natural enemies and a possible test bed for release of self-sustaining biocontrol agents
Fig. 1. Distribution of 2 fire ant microsporidian pathogens (Kneallhazia solenopsae, Vairimorpha invictae) and 2 fire ant viruses (SINV-1, SiDNV) among collections of the red imported fire ant, Solenopsis invicta, from islands in the West Indies. The fire ant RNA viruses SINV-2 and SINV-3 were not detected in any of the collections. The number of collections from monogyne colonies is shown over the total number of collections for each island or island group (Tortola [1/5], St. John [0/1], and St. Thomas [3/4]).
Fig. 1 in Long-term efficacy of two cricket and two liver diets for rearing laboratory fire ant colonies (Hymenoptera: Formicidae: Solenopsis invicta)
Fig. 1. Results of a 1 yr diet study using sugar water and either raw beef liver, raw chicken liver, or crickets to rear colonies of the imported fire ant Solenopsis invicta. A) Mean brood production rating of test colonies with brood: 4 = excel- lent, substantially more brood than workers; 3 = good, brood about equal to workers; 2 = poor, brood substantially less than workers; 1 = bad, only a little brood visible; and 0 = no brood. Colonies were fractionally rated if they ap- peared intermediate. Early in the study, about the end of Mar, we switched from domestic crickets (black squares) to banded crickets (crossed squares) and then back to domestic crickets (black squares) for 6 ant colonies on 6 Jun and then the remaining 7 colonies on 1 Jul. Colonies were eliminated from rating means when the queen died or brood production ceased. B) Percentage of test colonies containing brood plotted against time in months for colonies receiving either beef liver (N =10), chicken liver (N = 10), or crickets (N = 13).
Fig. 1 in Two Records of large specimens of Fire Salamander Salamandra salamandra (Linnaeus, 1758) (Amphibia: Caudata) in Bulgaria
Fig. 1. The observed adult female specimens of Fire Salamander (Salamandra salamandra) and their microhabitats. A&B – Chetirka River, 24.02.2015; C&D – Sheytanski Andak Stream, 03.03.2015.
Рис. 1. Δинамика чисΛенности меΛких мΛекопитающих в Цасучейском бору: 1 — суммарная чисΛенность (особей / 100 циΛинΑро-суток); Αоминирующие виΑы: 2 — забайкаΛьский хомячок, 3 — бурозубка тунΑряная, 4 — бурозубка крошечная, 5 — поΛёвка монгоΛьская, 6 — поΛёвка РаΑΑе, 7 — красная поΛёвка; A — остепнённый сосняк, B — первичная гарь, С — старая гарь, D — повторная гарь; стреΛка указывает время прохожΑения пожара. Ось X — гг., ось Y — чисΛенность Fig. 1. Population dynamics of small mammals in the Tsasucheysky Pine Forest: 1 — total abundance (individuals / 100 cylinder-days); dominant species: 2 — Cricetulus pseudogriseus, 3 — Sorex tundrensis, 4 — S. minutissimus, 5 — Alexandromys mongolicus, 6 — Lasiopodomys raddei, 7 — Myodes rutilus; A — steppe pine forest, B — primary burns site, С — old burns site; D — repeated burns site; the arrow indicates the time of the fire. The X-axis shows years; the Y-axis shows population density in Population dynamics of small mammals after spring fires in steppe pine forest
Рис. 1. Δинамика чисΛенности меΛких мΛекопитающих в Цасучейском бору: 1 — суммарная чисΛенность (особей / 100 циΛинΑро-суток); Αоминирующие виΑы: 2 — забайкаΛьский хомячок, 3 — бурозубка тунΑряная, 4 — бурозубка крошечная, 5 — поΛёвка монгоΛьская, 6 — поΛёвка РаΑΑе, 7 — красная поΛёвка; A — остепнённый сосняк, B — первичная гарь, С — старая гарь, D — повторная гарь; стреΛка указывает время прохожΑения пожара. Ось X — гг., ось Y — чисΛенность Fig. 1. Population dynamics of small mammals in the Tsasucheysky Pine Forest: 1 — total abundance (individuals / 100 cylinder-days); dominant species: 2 — Cricetulus pseudogriseus, 3 — Sorex tundrensis, 4 — S. minutissimus, 5 — Alexandromys mongolicus, 6 — Lasiopodomys raddei, 7 — Myodes rutilus; A — steppe pine forest, B — primary burns site, С — old burns site; D — repeated burns site; the arrow indicates the time of the fire. The X-axis shows years; the Y-axis shows population density
Fig. 3 in Post-fire effect of savannah vegetation on the establishment of new colonies of Atta sexdens rubropilosa (Hymenoptera: Formicidae)
Fig. 3. Characterization of Atta sexdens rubropilosa surviving colonies in burned and unburned areas, afer 120 d of queen reclusion (female), in soils from 2 depths (0.0–10.0 cm and 10.1–20.0 cm). Means (and standard errors) followed by the same letter did not differ from each other (ANOVA, P> 0.05)
Fig. 2 in Post-fire effect of savannah vegetation on the establishment of new colonies of Atta sexdens rubropilosa (Hymenoptera: Formicidae)
Fig. 2. Characterization of Atta sexdens rubropilosa surviving colonies in burned and unburned areas, afer 120 d of queen reclusion (female). Means (and standard errors) followed by the same letter did not differ from each other (ANOVA, P> 0.05).
Fig. 1 in Post-fire effect of savannah vegetation on the establishment of new colonies of Atta sexdens rubropilosa (Hymenoptera: Formicidae)
Fig. 1. Microbial activity (mean and standard error) in soils collected at 2 depths (0.0 to 10.0 cm and 10.1 to 20.0 cm) in areas with burned and unburned vegetation in Ipameri, GO, Brazil. Means followed by the same letter (accumulated CO2 production at 10 d), for each depth where the soil was collected, did not differ from each other (Mann–Whitney U test, P> 0.05).
Review of Emissions from Smouldering Peat Fires
<p>The file contains two table compilations of up-to-date inter-study of peat fire gas and particle emission factors (EFs) found in the scientific literature, both from laboratory and field studies. According to the geographical origins of the peat used in fire emission studies, we classified the samples into two categories: boreal and temperate peat (we merge these two climate zones into one category owing to the limited sampling location information reported in the literature), and tropical peat. By doing this, the best estimate peat fire EFs were calculated and compared between the two peat categories for the first time. It is hoped that the complied peat fire EFs can be used to improve the estimation of the total peat fire emission. </p> <p>This data was analysed in our journal paper paper:<br> Y. Hu, N. Fernandez-Anez, T. E. L. Smith, G. Rein, <strong>Review of Emissions from Smouldering Peat Fires and Their Contribution to Regional Haze Episodes</strong>, International Journal of Wildland Fire, 2018 (in press), DOI:10.1071/WF17084. </p>
Data from paper: "Life cycle of bamboo in the southwestern Amazon and its relation to fire events".
<p>This is the dataset from the paper "Life cycle of bamboo in the southwestern Amazon and its relation to fire events".</p> <p> </p> <p>It contains:</p> <p>- The processed MODIS (MAIAC) time series for the southwest Amazon, already processed and ready to use for the modeling (files such as bamboo_ts_annual_2000-2017_band[...]). MODIS (MAIAC) composites for south america is not provided here because of its huge file size (contact ricds@hotmail.com).</p> <p>- Final bamboo die-off data from 2001-2017 using the simple bilinear model (combination from band 2 and 5, p-value < 0.001). The data used for Figure S3. File: "Theoric_death_merged_band2_band5.tif"</p> <p>- Bamboo die-off detected from 2001-2017 using the simple bilinear model (files Theoric_death_year_band2 and Theoric_death_year_band5, and Theoric_pvalue_band2 and Theoric_pvalue_band5). To obtain the same map as in the paper, must apply the p < 0.001 over the death year map.</p> <p>- Bamboo spatial distribution obtained by the die-off detection and live detection. In this map, values equal to 0, 1 and 2 correspond to non-bamboo, live bamboo and dead bamboo forests.</p> <p>- Bamboo die-off predictions from 2000-2028 using the empirical curves (files Empirical_death_year_band2_curves2 and Empirical_death_year_band5_curves2, and Empirical_p_value_band5_curves2 and Empirical_p_value_band5_curves2). To obtain the same map as in the paper, must apply the p < 0.001 over the death year map.</p> <p> </p> <p>More information contact Ricardo Dalagnol (ricds@hotmail.com).</p>
FlowBlaze on Fed4FIRE+ FB-FIRE Final Results of the Experiment
<p>This repository contains the results of the FB-FIRE experiment. The aim of FB-FIRE is to test, validate and assess in the Fed4FIRE+ Virtual Wall testbed the performance of FlowBlaze, a novel stateful programmable dataplane engine that can simplify network functions (NF) design and implementation, while providing high performance packet forwarding, and support for future hardware offloading to SmartNICs. FlowBlaze is an abstraction that can be implemented in an efficient DPDK-accelerated software engine, conceived to rapidly design and deploy complex network functions hiding the complexity of software optimizations associated to the development of network functions.</p>
Figure 1 in The History of Little Fire Ant Wasmannia auropunctata Roger in the Hawaiian Islands: Spread, Control, and Local Eradication
Figure 1. Number of known locations infested with Wasmannia auropunctata on Hawaii island between 1999 and 2007. Data sourced from Conant and Hirayama (2000); Motoki et al. (Motoki et al. 2013), P. Conant (pers. com.) and informal reports from Hawaii Department of Agriculture.
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Allen Brain Atlas
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DANDI Archive for NWB datasets
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