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Fig. 3 in Javan mongoose (Herpestes javanicus) abundance and spatial ecology in a degraded dry dipterocarp forest
Fig. 3. Map of Sakaerat Biosphere Reserve with radio tracked (December 2019 to January 2021) Javan mongoose (Herpestes javanicus) home ranges and prey grids (PG). 95% utilisation contours (U.C) for male (M6, M1) and female (F1) mongooses are labelled in the legend. 50% U.C are solid line circles within each individual's home range. Prey grids collected ground-dwelling invertebrate mass as well as rodent biomass within the DDF (October to December 2020). Stars indicate where only ground-dwelling invertebrates were collected. Triangles indicate areas where sweep netting for invertebrates occurred in addition to sampling for rodent biomass and ground-dwelling invertebrates.
Fig. 1 in Javan mongoose (Herpestes javanicus) abundance and spatial ecology in a degraded dry dipterocarp forest
Fig. 1. Map and location of Sakaerat Biosphere Reserve with camera trap stations used to estimate Javan mongoose (Herpestes javanicus) abundance in 2017. Prey grid stations were used to calculate yearly averaged rodent biomass from January 2017 to November 2017.
Figure 4 in Karyological and some morphological characteristics of the Egyptian mongoose, Herpestes ichneumon (Mammalia: Carnivora), along with current distribution range in Turkey
Figure 4. Skull morphology of H. ichneumon from Hatay: A) dorsal, B) ventral, C) lateral view of the skull; D) mandible (lingual), E) mandible (labial) view.
Figure 1 in Karyological and some morphological characteristics of the Egyptian mongoose, Herpestes ichneumon (Mammalia: Carnivora), along with current distribution range in Turkey
Figure 1. Distribution of Herpestes ichneumon in Turkey. ▲: Selçuk (Danford and Alston, 1877); ◇◆: Bahçe (Gülen, 1971); ★: current distribution recorded during this study. 1) Göksu Delta; 2) Tarsus, near the Mersin–Adana highway; 3) 1 km west of Tabaklar village; 4) 7 km northeast of Kefeli village; 5) 2 km west of Gölyaka village; 6) 3 km south of Adana; 7) 3 km southeast of Adana; 8) 1 km southeast of Menekşe village; 9) 3 km south of Deveciuşağı village (sample no. 2429); 10) near Sakarcalı village; 11) near Yeniköy village; 12) 1 km east of Cevdetiye village; 13) 2 km north of Ahrazlar village; 14) 1 km east of Hasanlı village (sample no. 19); 15) 1 km west of Kapısuyu village; and 16) 1 km south of Emirler village (Karaisalı).
Figure 3 in Seasonal hormones, female reproductive tract changes, and some field observations on breeding activities of the small Indian mongoose (Herpestes javanicus) from its native range of Potohar Plateau, Pakistan
Figure 3. Light microscopic (hematoxylin and eosin stained) sections (40×) of the ovaries of female small Indian mongoose (Herpestes javanicus) from the Potohar Plateau, Pakistan: A) showing 3 Graafian follicles indicative of the state of preovulation during February 2013; B) events of early gestation period during March 2013, corpus luteum of moderate size and reddish yellow, antrum being a bit convoluted in structure rather than being complete; C) events of late gestation period during April 2013, whereby corpora lutea are seen as the most prominent structures; D) showing lactation phase of the species with no corpora lutea or ripe follicles during June 2013. (*P.F.: primary follicle; S.F.: secondary follicle; C.L.: corpus luteum; G.F.: Graafian follicle; Pr. F.: primordial follicle).
Figure 4. A in Seasonal hormones, female reproductive tract changes, and some field observations on breeding activities of the small Indian mongoose (Herpestes javanicus) from its native range of Potohar Plateau, Pakistan
Figure 4. A) Foot prints of small Indian mongoose established around its burrow, B) Especially designed mesh trap for live capturing of the species, C) Placental Scars, D) Developing embryos inside the uteri of female mongoose exposed after dissection, E) A vigilant mongoose, F) Small Indian mongoose and her pups caught in a live trap
Figure 2 in Seasonal hormones, female reproductive tract changes, and some field observations on breeding activities of the small Indian mongoose (Herpestes javanicus) from its native range of Potohar Plateau, Pakistan
Figure 2. Levels (mIU/mL) of follicle stimulating hormone (FSH) and luteinizing hormone (LH) in plasma samples of small Indian mongoose females (Herpestes javanicus) trapped on the Potohar Plateau. LH levels show 2 peaks (1 in September 2012 and 1 in March 2013).
Figure 3 in Human activity mediates reciprocal distribution and niche separation of two sympatric mongoose species on the Pothwar Plateau, Pakistan
Figure 3. Photomicrographs of whole mounts of hair structure of three rodent species (recovered from fecal samples and reference hairs) consumed by the small Indian mongoose on the Pothwar Plateau. A) Whole mount of recovered hair of Rattus rattus, B) Whole mount of reference hair of Rattus rattus, C) Whole mount of recovered hair of Nesokia indica, D) Whole mount of reference hair of Nesokia indica, E) Whole mount of recovered hair of Mus musculus, F) Whole mount of reference hair of Mus musculus.
Figure 2 in Human activity mediates reciprocal distribution and niche separation of two sympatric mongoose species on the Pothwar Plateau, Pakistan
Figure 2. Average length (cm), mass (g), and diameter (cm) of SIM and GM fecal samples collected from study sites on the Pothwar Plateau.
Figure 5 in Human activity mediates reciprocal distribution and niche separation of two sympatric mongoose species on the Pothwar Plateau, Pakistan
Figure 5. Prey species richness (S), diversity index (H'), and evenness index (E) of the prey species of the small Indian mongoose (Herpestes javanicus) on the Pothwar Plateau during the current study period.
Figure 1 in Human activity mediates reciprocal distribution and niche separation of two sympatric mongoose species on the Pothwar Plateau, Pakistan
Figure 1. GIS-based map showing distribution of the two mongoose species (Herpestes javanicus and H. edwardsii)
Figure 4 in Human activity mediates reciprocal distribution and niche separation of two sympatric mongoose species on the Pothwar Plateau, Pakistan
Figure 4. Photomicrographs of whole mount of hair structure of five different rodent species (recovered from fecal samples of gray mongoose and reference hair of rodents) consumed by the gray mongoose; A) Whole mount of recovered hair of Golunda ellioti, B) Whole mount of reference hair of Golunda ellioti, C) Whole mount of recovered hair of Tetera indica, D) Whole mount of reference hair of Tetera indica, E) Whole mount of recovered hair of Nesokia indica, F) Whole mount of reference hair of Nesokia indica, G) Whole mount of recovered hair of Rattus rattus, H) Whole mount of reference hair of Rattus rattus, I) Whole mount of recovered hair of Mus musculus, J) Whole mount of reference hair of Mus musculus.
Fig. 2 in Molecular detection and characterization of Leishmania infantum in free- ranging Egyptian mongoose (Herpestes ichneumon)
Fig. 2. Maximum Likelihood (ML) phylogenetic tree of 27 L. infantum nucleotide sequences (410 nt long in the final dataset, including gaps), obtained during this study (MH799321) and others available in GenBank, based on the Hasegawa-Kishino-Yano model (HKY) (Hasegawa et al., 1985). The tree with the highest log likelihood (−1026.87) is shown. Initial tree(s) for the heuristic search were obtained automatically by applying Neighbor-Join and BioNJ algorithms to a matrix of pairwise distances estimated using the Maximum Composite Likelihood (MCL) approach, and then selecting the topology with superior log likelihood value. A discrete Gamma distribution was used to model evolutionary rate differences among sites (5 categories (+G, parameter = 0.3289) (HKY + G). The tree was drawn to scale, with branch lengths measured in the number of substitutions per site. Robustness of the tree nodes was assessed by bootstrapping 1000 times. The graphical edition of the phylogenetic tree was performed with tree explorer, MEGA7 software (Kumar et al., 2016). Only bootstrap (BS) values equal or greater than 70 are shown on the tree, with the exception of the MH799321 cluster wherein the Bs values, although <70, are displayed for the reader. A 2-letter code and a specific colour (Top left) was attributed to each country for better identification of the origin of each strain. Whenever possible, the host was identified by a specific shape (Top left), namely dog (Canis lupus familiaris, star), human (Homo sapiens, triangle), Egyptian mongoose (Herpestes ichneumon, square) and hoary fox (Lycalopex vetulus, diamond). Sampling dates are indicated, whenever available. (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 detection and characterization of Leishmania infantum in free- ranging Egyptian mongoose (Herpestes ichneumon)
Fig. 1. Spatial distribution of wild carnivore samples in mainland Portugal. Administrative regions at the district level are indicated. The overall proportion of samples per district is indicated by the grey scale. The abbreviatures of districts are as follows: Viana do Castelo (VC), Braga (BR), Vila Real (VR), Bragança (BG), Porto (PT), Aveiro (AV) Viseu (VS), Guarda (GR), Coimbra (CM), Castelo Branco (CB), Leiria (LR), Santarém (SA), Portalegre (PA), Lisboa (Lx), Setúbal (ST), Évora (EV), Beja (BJ) and Faro (FR). White circles with numbers in red specify the number and location of Egyptian mongooses that were kDNA-positive by PCR. (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 Conservation Status Of Small Asian Mongoose Herpestes Javanicus (É. Geoffroy Saint-Hilaire, 1818) (Mammalia: Carnivora: Herpestidae) In Lao Pdr
Fig. 1. Lao PDR, with locations of post-1990 Small Asian Mongoose records, survey areas, and sites mentioned in the text. Filled stars: confirmed records; open stars: provisional records. Increasing altitude is represented by increasing darkness: areas of level terrain are therefore areas of uniform shading. Dotted outlines indicate national protected areas (all surveyed to at least some extent). Survey areas outside NPA system: A, Phongsali town and surrounds; B, Upper Lao Mekong and Bokeo plain; C, Xiangkhouang plateau, Phou (= Mount) Gnouan and Phou San; D, Muang (= District) Sangthong, Vientiane municipality; E, Nam Theun Extension proposed NPA (= former Nam Chat–Nam Phan provincial protected area); F, Pakxan wetlands; G, Nakai plateau; H, Muang Vilabouli, Savannakhet province; I, western Savannakhet lowlands and Mekong; J, central Savannakhet lowlands; K, Phou Ahyon; L, Dakchung plateau; M, Salavan town and surrounds; N, Phou Kathong proposed NPA; O, Xe (= River) Namnoy catchment and Bolaven Southwest proposed NPA; P, Muang Pathoumphon, Champasak province; Q, Nam Ghong provincial protected area; R, Dong Khanthung proposed NPA. In addition various sites around Vientiane received at least moderate coverage.
Data from: Social and seasonal variation in dwarf mongoose home-range size, daily movements and burrow use
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Figure 5. H in Karyological and some morphological characteristics of the Egyptian mongoose, Herpestes ichneumon (Mammalia: Carnivora), along with current distribution range in Turkey
Figure 5. H. ichneumon observed in Karataş-Adana on September 2002 (Photo: Şakir Önder Özkurt).
Figure 2 in Karyological and some morphological characteristics of the Egyptian mongoose, Herpestes ichneumon (Mammalia: Carnivora), along with current distribution range in Turkey
Figure 2. Metaphase plate of a male H. ichneumon from Hatay.
Collective self-assessment in banded mongoose intergroup contests
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Data from: High ambient temperatures are associated with reduced foraging capacity in an equatorial mammal, the banded mongoose (Mungos mungo)
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International Brain Laboratory public data
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