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Fig. 1 in Is parasite load dependent on host aggregation size? The case of the greater mouse-eared bat Myotis myotis (Mammalia: Chiroptera) and its parasitic mite Spinturnix myoti (Acari: Gamasida)
Fig. 1 Distribution of greater mouse-eared bat (Myotis myotis) maternity aggregations (grey circles) and single founding individuals (black dots) in the Beskids (Carpathian Mountains, Poland). Data pooled from Kozakiewicz (2003), Szkudlarek et al. (2008), and our data. For the investigated maternity colonies, forested areas within a 10-km radius is shown
Fig. 3 in Is parasite load dependent on host aggregation size? The case of the greater mouse-eared bat Myotis myotis (Mammalia: Chiroptera) and its parasitic mite Spinturnix myoti (Acari: Gamasida)
Fig. 3 Proportions of protonymph (PN), deutonymph (DN), and adult (AD) stages of S. myoti mites, collected from Myotis myotis (bars), and the sex ratios of deutonymph and adult mites (circles)
Fig. 2 in Is parasite load dependent on host aggregation size? The case of the greater mouse-eared bat Myotis myotis (Mammalia: Chiroptera) and its parasitic mite Spinturnix myoti (Acari: Gamasida)
Fig. 2 Micrograph of the adult female Spinturnix myoti, dorsal view. Scanning electron microscopy image, original magnification ×40
Fig. 3 in Ectoparasites are unlikely to be a primary cause of population declines of bent-winged bats in south-eastern Australia
Fig. 3. Ventral view of idiosoma of female Spinturnix loricata. Rectangle in inset photograph denotes position of sternal shield. Note elongate sternal shield (Arrow).
Fig. 4 in Ectoparasites are unlikely to be a primary cause of population declines of bent-winged bats in south-eastern Australia
Fig. 4. Ventral view of idiosoma of female Spinturnix psi. Rectangle in inset photograph denotes position of sternal shield. Note subcircular sternal shield (Arrow).
A Corpus-driven Study of Contrastive Markers in Cantonese‒English Political Interpreting-Figure 1. The frequency of different renditions of "bat gwo" in the English sub-corpus
<p>The renditions of bat gwo and daan (hai) were closely examined by looking into how they were interpreted. Figure 1 lists all the renditions of bat gwo and their frequency. The figures show that bat gwo was most often interpreted into however (frequency=22) — its closest equivalence in English. There were, however, 7 cases that bat gwo was interpreted into but — its stronger and less subtle correspondence that indicates denial and contrast. Apart from rendering into these two most common English contrastive markers, there were also 5 cases that bat gwo was not interpreted at all, suggesting a possible mitigation strategy employed by the interpreter(s). Likewise, the rest of bat gwo were rendered into other markers including nevertheless, nonetheless, while, yet, having said that / that said, all of which indicate concession and topic change, yet with an even higher degree of subtlety as compared to however.</p>
Dataset (encounter histories of female bats) used in the analysis for the paper Culina et al.: Live fast, don't die young: survival reproduction trade-offs in long-lived income breeders
<p>Two data files (Md_capture_H, Mn_capture_H) represent the capture histories of females of two species (Myotis daubentonii = Md, and M. nattereri=Mn). These capture histories were used to run multi-event-capture-mark-recapture model, as described in the paper, and in the readme document in this data package.<br> </p>
Data from: Defensive fruit metabolites obstruct seed dispersal by altering bat behavior and physiology at multiple temporal scales.
<p>These data support the publication "Defensive fruit metabolites obstruct seed dispersal by altering bat behavior and physiology at multiple temporal scales".</p>
Impacts of rainforest degradation on the diets of the insectivorous bats of Sabah
<b>Description: </b><p>The work was carried out within Sabah, at the SAFE project, Danum Valley and Maliau basin. Bats were captured by deploying 6 harp traps per night, during field seasons taking place in 2015, 2016 and 2017. Bat guano samples were collected by placing individual bats into cloth bags, and then releasing them after 12 hours. Any guano in the bottom of the bag was then transferred into 95% ethanol and stored at -20. DNA was extracted from the faecal samples using a Qiagen Stool Mini kit, and then amplified using the ZBJ-ArtF1c ZBJ-ArtR2c primers, and sequencing the DNA on an Illumina MiSeq.</p><p><b>Project: </b>This dataset was collected as part of the following SAFE research project: <a href="https://www.safeproject.net/projects/project_view/182"><b>Impacts of rainforest degradation on the diets of the insectivorous bats of Sabah</b></a></p><p><b>Funding: </b>These data were collected as part of research funded by: </p><ul><li>NERC (Standard grant, NE/K016407/1)</li><li>Royal Society (Standard grant, RG130793)</li><li>Bat Conservation International (Standard grant)</li></ul><p>This dataset is released under the CC-BY 4.0 licence, requiring that you cite the dataset in any outputs, but has the additional condition that you acknowledge the contribution of these funders in any outputs.</p><p></p><p><b>Permits: </b>These data were collected under permit from the following authorities:</p><ul><li>Sabah Biodiversity Centre (Research licence JKM/MBS.1000-2/2 JLD.4 (46))</li></ul><p></p><p><b>XML metadata: </b>GEMINI compliant metadata for this dataset is available <a href="https://www.safeproject.net/datasets/xml_metadata?id=3247465">here</a></p><p><b>Files: </b>This dataset consists of 3 files: Bat_SAFE_data_metadata.xlsx, interaction_network.csv, sequences_95.fasta</p><p><b>Bat_SAFE_data_metadata.xlsx</b></p><p>This file contains dataset metadata and 1 data tables:</p><ol><li><p><b>data</b> (described in worksheet Data)</p><p>Description: measurements collected</p><p>Number of fields: 21</p><p>Number of data rows: 3292</p><p>Fields: </p><ul><li><b>TrapName</b>: The trap ID which the bats were captured in (Field type: ID)</li><li><b>Lat</b>: Latitude of trap (Field type: Latitude)</li><li><b>Long</b>: Longitude of trap (Field type: Longitude)</li><li><b>Elevation</b>: Elevation of trap (Field type: Numeric)</li><li><b>Bat_no</b>: Bat ID (Field type: ID)</li><li><b>Date</b>: Date of capture (Field type: Date)</li><li><b>Faeces_no1</b>: Tube number used to store faecal sample. Pairs up with column names of interaction matrix (Field type: ID)</li><li><b>Faeces_no2</b>: Number of any additional faeces (Field type: ID)</li><li><b>Biopsy_Dave</b>: Tube used to store wing biopsy (Field type: ID)</li><li><b>Block</b>: If sampling occurred within the SAFE landscape, this is the block it occurred within (Field type: ID)</li><li><b>Fragment</b>: If sampling occurred within the SAFE landscape, this is the fragment size it occurred within (Field type: ID)</li><li><b>Site</b>: The site within Sabah sampling occurred at (Field type: ID)</li><li><b>Species</b>: The bat species ID (Field type: Taxa)</li><li><b>Sex</b>: Male or Female (Field type: Categorical trait)</li><li><b>Age</b>: Was the bat an adult or juvenile (Field type: Categorical trait)</li><li><b>Forearm</b>: The forearm length of the bat (Field type: Numeric trait)</li><li><b>Weight</b>: The weight of the bat (Field type: Numeric Trait)</li><li><b>Reproductive_condition</b>: If a female bat, if the bat was Non-Reproductive, PRegnant, LActating or Post-Lactating (Field type: Categorical trait)</li><li><b>Parasite</b>: Tube used to store any ectoparasites obtained (Field type: ID)</li><li><b>Time</b>: If the bat was captured in evening or morning (Field type: Categorical)</li><li><b>Tag</b>: Band ID, if used (Field type: ID)</li></ul></li></ol><p><b>interaction_network.csv</b></p><p>Description: A network of operational taxonomic units found within the guano of bats captured in Sabah. The column names refer to the bat guano id, as found in the columns 'Faeces_no1' and 'Faeces_no2' in the fieldwork data, and the rownames refer to the OTU of the prey, which is paired to the names of the OTUs in the fasta file.</p><p><b>sequences_95.fasta</b></p><p>Description: A fasta file of prey OTUs found in bat guano, generated using 95% similarity for clustering. The sequence names correspond with the rownames of the file interaction_network.csv</p><p><b>Date range: </b>2015-02-16 to 2017-07-21</p><p><b>Latitudinal extent: </b>4.5000 to 5.0933</p><p><b>Longitudinal extent: </b>116.7500 to 117.8380</p><p><b>Taxonomic coverage: </b><br> All taxon names are validated against the GBIF backbone taxonomy. If a dataset uses a synonym, the accepted usage is shown followed by the dataset usage in brackets. Taxa that cannot be validated, including new species and other unknown taxa, morphospecies, functional groups and taxonomic levels not used in the GBIF backbone are shown in square brackets.</p><div>Animalia<br> - Chordata<br> -  - Mammalia<br> -  -  - Chiroptera<br> -  -  -  - Emballonuridae<br> -  -  -  -  - <i>Emballonura</i><br> -  -  -  -  -  - <i>Emballonura alecto</i><br> -  -  -  -  -  - <i>Emballonura monticola</i><br> -  -  -  - Hipposideridae<br> -  -  -  -  - <i>Hipposideros</i><br> -  -  -  -  -  - <i>Hipposideros ater</i><br> -  -  -  -  -  - <i>Hipposideros bicolor</i><br> -  -  -  -  -  - <i>Hipposideros cervinus</i><br> -  -  -  -  -  - <i>Hipposideros diadema</i><br> -  -  -  -  -  - <i>Hipposideros doriae</i><br> -  -  -  -  -  - <i>Hipposideros dyacorum</i><br> -  -  -  -  -  - <i>Hipposideros galeritus</i><br> -  -  -  -  -  - <i>Hipposideros ridleyi</i><br> -  -  -  - Megadermatidae<br> -  -  -  -  - <i>Megaderma</i><br> -  -  -  -  -  - <i>Megaderma spasma</i><br> -  -  -  - Nycteridae<br> -  -  -  -  - <i>Nycteris</i><br> -  -  -  -  -  - <i>Nycteris tragata</i><br> -  -  -  - Pteropodidae<br> -  -  -  -  - <i>Balionycteris</i><br> -  -  -  -  -  - <i>Balionycteris maculata</i><br> -  -  -  -  - <i>Macroglossus</i><br> -  -  -  -  -  - <i>Macroglossus minimus</i><br> -  -  -  -  - <i>Megaerops</i><br> -  -  -  -  -  - <i>Megaerops wetmorei</i><br> -  -  -  - Rhinolophidae<br> -  -  -  -  - <i>Rhinolophus</i><br> -  -  -  -  -  - <i>Rhinolophus acuminatus</i><br> -  -  -  -  -  - <i>Rhinolophus affinis</i><br> -  -  -  -  -  - <i>Rhinolophus borneensis</i><br> -  -  -  -  -  - <i>Rhinolophus creaghi</i><br> -  -  -  -  -  - <i>Rhinolophus luctus</i><br> -  -  -  -  -  - <i>Rhinolophus sedulus</i><br> -  -  -  -  -  - <i>Rhinolophus trifoliatus</i><br> -  -  -  - Vespertilionidae<br> -  -  -  -  - <i>Harpiocephalus</i><br> -  -  -  -  -  - <i>Harpiocephalus harpia</i><br> -  -  -  -  - <i>Hesperoptenus</i><br> -  -  -  -  -  - <i>Hesperoptenus blanfordi</i><br> -  -  -  -  - <i>Kerivoula</i><br> -  -  -  -  -  - <i>Kerivoula hardwickii</i><br> -  -  -  -  -  - <i>Kerivoula intermedia</i><br> -  -  -  -  -  - <i>Kerivoula lenis</i><br> -  -  -  -  -  - <i>Kerivoula minuta</i><br> -  -  -  -  -  - <i>Kerivoula papillosa</i><br> -  -  -  -  -  - <i>Kerivoula pellucida</i><br> -  -  -  -  -  - <i>Kerivoula whiteheadi</i><br> -  -  -  -  - <i>Murina</i><br> -  -  -  -  -  - <i>Murina aenea</i><br> -  -  -  -  -  - <i>Murina cyclotis</i><br> -  -  -  -  -  - <i>Murina rozendaali</i><br> -  -  -  -  -  - <i>Murina suilla</i><br> -  -  -  -  - <i>Myotis</i><br> -  -  -  -  -  - <i>Myotis muricola</i><br> -  -  -  -  -  - <i>Myotis ridleyi</i><br> -  -  -  -  - <i>Phoniscus</i><br> -  -  -  -  -  - <i>Phoniscus atrox</i><br> -  -  -  -  - <i>Pipistrellus</i><br> -  -  -  -  -  - <i>Pipistrellus javanicus</i><br> -  -  -  -  -  - <i>Pipistrellus tenuis</i><br> -  -  -  -  - <i>Scotophilus</i><br> -  -  -  -  -  - <i>Scotophilus kuhlii</i><br></div><p></p>
Fig. 23 in Bats Of Central Ukraine: A Synopsis
Fig. 23. Bat species of Central Ukraine by number of localities in 1999–2021, according to: a, own data; b, sum of all available geographically attributed data for the time period.
Fig. 18 in Bats Of Central Ukraine: A Synopsis
Fig. 18. Record localities of Pipistrellus pygmaeus (A, B), P. pipistrellus s. s. (C), and P. pipistrellus s. l. (D).
Fig. 1 in Bats Of Central Ukraine: A Synopsis
Fig. 1. Study area and localities (nloc = 265). A — data of other authors, 1848–2020 (nloc = 134); B — own data, 1999–2021 (nloc= 168). Subregions, here and further: 1, mixed forests, or Polissia (ZMF); 2, forest-steppe (ZFS); 3, the Dniester River (DRS); see text.
Fig. 10 in Bats Of Central Ukraine: A Synopsis
Fig. 10. Record localities of Myotis brandtii (A, B), Myotis alcathoe (C), and not identidied specimens of Myotis mystacinus morphogroup (D).
Figure 1 in Bat species diversity from Reserva Ecológica de Guapiaçu, Rio de Janeiro, Brazil: a compilation of two decades of sampling
Figure 1. Location of Reserva Ecológica de Guapiaçu (red/white circle) in the context of the Atlantic Forest remnants of Rio de Janeiro (green), Southeastern Brazil. Shapefile of forest coverage is from the Brazilian NGO SOS Mata Atlântica database.
Figure 2 in Local concentration of foraging noctule bats (Nyctalus noctula) as a possible tool to assess the density of bats in large forest complexes
Figure 2. Insects (white dots) in camera flash at the observation point (lens directed vertically into the sky).
Figure 3 in Local concentration of foraging noctule bats (Nyctalus noctula) as a possible tool to assess the density of bats in large forest complexes
Figure 3. Fluctuation in daily temperature 1 month before and after the first observation (2 July 2012). Black arrows show dates of the first and second controls.
Fig. 3 in Molecular characterization and phylogenetic analysis of Trypanosoma spp. detected from striped leaf-nosed bats (Hipposideros vittatus) in Zambia
Fig. 3. Species delimitation of Trypanosoma cruzi clade. Maximum likelihood phylogeny with outgroup (Trypanosoma lewisi) and with Baysian support values presented 17 linages recognized as species for the PTP analysis. Monophyletic groups in red indicated single putative species as well as terminal branches in blue.. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 1 in Molecular characterization and phylogenetic analysis of Trypanosoma spp. detected from striped leaf-nosed bats (Hipposideros vittatus) in Zambia
Fig. 1. Giemsa staining of Trypanosoma sp. from ZB17–105 in BSK-M medium Representative images of ZB17-105 in the BSK-M medium are displayed at the same magnification (x1000). (a,b) flagellates resembling promastigote forms. (c) possibly epimastigote forms under division. K: kinetoplast, N: nucleus, F: flagellum.
Figure 3. The 95 in Effects of agroecosystems on insect and insectivorous bat activity: a preliminary finding based on light trap and mist net captures
Figure 3. The 95% family-wise confidence level for multiple comparisons test based on insectivorous bat species analyses. Left: H. aff. ruber; right: H. jonesi.
Figure 2. The 95 in Effects of agroecosystems on insect and insectivorous bat activity: a preliminary finding based on light trap and mist net captures
Figure 2. The 95% family-wise confidence level for multiple comparisons test based on insect order analyses. Left: Lepidoptera; right: Diptera.
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