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Fig. 1 in Effects of latitude, host body size, and host trophic guild on patterns of diversity of helminths associated with humans, wild and domestic mammals of Mexico

Fig. 1. Maps showing the geographic locations of the records, classified by phylum of the subsetted database.

opencc-by-4.0Apr 2020View details →

Fig. 2 in Prevalence of protozoan parasites in small and medium mammals in Texas, USA

Fig. 2. Phylogenetic tree of 18S rRNA gene sequence alignments for Hepatozoon spp. purified from this study (*) and relevant host species extracted from GenBankṜ. In parenthesis are referenced all the GenBankṜ accession numbers of the sequences used to generate this tree. Hepatozoon sp. Sequences detected in this study: M064 = GenBankṜ MN012924; M333 = GenBankṜ MN012925; M006 = GenBankṜ MN012926; M051 = GenBankṜ MN012927; M318 = GenBankṜ MN012928; M468 = GenBankṜ MN012929; M472 = GenBankṜ MN012930; M118 = GenBankṜ MN012931.

opencc-by-4.0Apr 2020View details →

Fig. 1 in Prevalence of protozoan parasites in small and medium mammals in Texas, USA

Fig. 1. Phylogenetic tree of 18S rRNA gene sequence alignments for Babesia spp. purified from this study (*) and relevant host species extracted from GenBankṜ. In parenthesis are referenced all the GenBankṜ accession numbers of the sequences used to generate this alignment. As a note, the Babesia Spanish Dog isolate (AY534602) is now reffered to as B. vulpes. Babesia microti -like sequences from this study: M001 = GenBankṜ MN011931; M006 = GenBankṜ MN011932; M050 = GenBankṜMN011933; M051 = GenBankṜ MN011934; M052 = GenBankṜ MN011935. Babesia sp Coco in this study M001 = GenBankṜ MN013190. Babesia sp: M052 = GenBankṜ MN013191.

Fig. 2 in Small-mammal characteristics affect tick communities in southwestern Tennessee (USA)

Fig. 2. Mean number of ticks per host by sex and age of rodent hosts (Peromyscus leucopus, Sigmodon hispidus, Peromyscus maniculatus, Microtus pinetorum, and Ochrotomys nuttalli) captured at Hobart Ames Plantation, Fayette and Hardeman counties, Tennessee.

Fig. 1 in Small-mammal characteristics affect tick communities in southwestern Tennessee (USA)

Fig. 1. Number of ticks present on rodent hosts (Peromyscus leucopus, Sigmodon hispidus, Peromyscus maniculatus, Microtus pinetorum, and Ochrotomys nuttalli) captured at the Hobart Ames Plantation, Fayette and Hardeman counties, Tennessee. (a) Number of ticks by host sex x weight interaction (males y = 0.009x + 2.135; females y = 0.022x - 0.09). (b) Number of ticks by host age x weight interaction (adult y = 0.051x + 0.203; subadult = 0.310x - 3.499).

Fig. 7 in Mammal parasites in arid Australia

Fig. 7. Distributions of selected endemic species of hydromyine rodents in Australia for which published helminthological studies are available. A, Distributions of the grassland melomys, Melomys burtoni, the fawn-footed melomys, M. cervinipes and the white-tailed rat, Uromys caudimaculatus; B, Distributions of the delicate mouse, Pseudomys delicatulus and the sandy inland mouse, P. hermansburgensis; C, Distributions of the eastern chestnut mouse, P. gracilicaudatus and the desert mouse, P. desertor.

Fig. 5 in Mammal parasites in arid Australia

Fig. 5. Geographical distributions of the closely related strongylid nematode species Rugopharynx australis and R. macropodis. Records based on Beveridge and Chilton (1999) and voucher specimens deposited in the South Australian Museum, Adelaide. Rugopharynx australis (represented by closed circles) occurs in the stomachs of Macropus fuliginosus, M. giganteus, Osphranter rufus and O. robustus; R. macropodis (represented by open squares) occurs in the stomachs of M. fuliginosus and M. giganteus.

Fig. 3 in Mammal parasites in arid Australia

Fig. 3. Geographical distributions of the arid adapted kangaroos, the red kangaroo (Osphranter rufus) (A) and the euro (Macropus robustus erubescens) (B) with its related sub-species, the eastern wallaroo (M. r. robustus) and the northern wallaroo (M. r. woodwardi), occurring in higher rainfall areas to the east and north of the arid zone respectively. Named localities are sites at which epidemiological studies of the parasites of these kangaroo species have been undertaken.

Fig. 2 in Mammal parasites in arid Australia

Fig. 2. Geographical distributions of the rain-forest adapted pademelons (Thylogale spp.: Macropodidae) (A) and the grey kangaroos (Macropus fuliginosus and M. giganteus (Macropodidae) (B), with ranges of the latter two species extending into the semi-arid and arid ranges of the continent. Named localities are sites at which epidemiological studies of the parasites of these kangaroo species have been undertaken.

Fig. 4 in Mammal parasites in arid Australia

Fig. 4. Geographical distributions of species of rock wallaby (Petrogale) (Macropodidae) in eastern Australia, comparing that of the rain-forest inhabiting P. persephone, with the closely related members of the P. penicillata species complex (P. assimilis, P. inornata, P. godmani, P. mareeba, P. penicillata, P. sharmani) occurring in a parapatric pattern along the east coast, and P. purpureicollis, the most arid-adapted species.

Fig. 2 in Investigation of Bartonella spp. in brazilian mammals with emphasis on rodents and bats from the Atlantic Forest

Fig. 2. Phylogenetic relationships within the Bartonella genus based on the groEL gene. The tree was inferred by using the Maximum Likelihood (ML) and Bayesian inference (BI) with the HKY + I + G model. The nodal support is described at the left by bootstrap replicates and at the right by posterior probability to each node represented. The symbol of one asterisk (*) indicates low nodal support in ML or BI, and the symbol of two asterisk (**) indicates incongruence between ML and BI. The sequences detected in the present study are described in red and the sequences of previous studies of Brazilian genotypes in blue. The highlighted clades represented the genotypes described to Brazil. The clade E, F and G represent the genotypes obtained in this study. Brucella abortus and Ca. Tokpelaia hoelldoblerii was used as an outgroup. (For interpretation of the references to color in this figure legend, the reader is referred to the Web version of this article.)

Fig. 3 in Investigation of Bartonella spp. in brazilian mammals with emphasis on rodents and bats from the Atlantic Forest

Fig. 3. Phylogenetic relationships within the Bartonella genus based on the ftsZ gene. The tree was inferred by using the Maximum Likelihood (ML) and Bayesian inference (BI) with the GTR + I + G model. The nodal support is described at the left by bootstrap replicates and at the right by posterior probability to each node represented. The symbol of one asterisk (*) indicates low nodal support in ML or BI, and the symbol of two asterisk (**) indicates incongruence between ML and BI. The sequences detected in the present study are described in red and the sequences of previous studies of Brazilian genotypes in blue. The highlighted clades represented the genotypes described to Brazil. The clade H, I, J, K and L represent the genotypes obtained in this study. Brucella abortus and Ca. Tokpelaia hoelldoblerii was used as an outgroup. (For interpretation of the references to color in this figure legend, the reader is referred to the Web version of this article.)

Fig. 1 in Investigation of Bartonella spp. in brazilian mammals with emphasis on rodents and bats from the Atlantic Forest

Fig. 1. Phylogenetic relationships within the Bartonella genus based on the gltA gene. The tree was inferred by using the Maximum Likelihood (ML) and Bayesian inference (BI) with the GTR + I + G model. The nodal support is described at the left by bootstrap replicates and at the right by posterior probability to each node represented. The symbol of one asterisk (*) indicates low nodal support in ML or BI, and the symbol of two asterisk (**) indicates incongruence between ML and BI. The sequences detected in the present study are described in red and the sequences of previous studies of brazilian genotypes in blue. The highlighted clades represented the genotypes described to Brazil. The clade A, B, C and D represent the genotypes obtained in this study. Brucella abortus and Ca. Tokpelaia hoelldoblerii was used as an outgroup. (For interpretation of the references to color in this figure legend, the reader is referred to the Web version of this article.)

opencc-by-4.0Aug 2013View details →

Fig. 2 in Camera-Trapping Survey Of Mammals In And Around Imbak Canyon Conservation Area In Sabah, Malaysian Borneo

Fig. 2. The observed species accumulation curve (-o-) and 95% CIs (---) for mammalian species in and around Imbak Canyon Conservation Area. The curve was constructed using abundancebased rarefaction approach (i.e., by using the number of independent photographs captured) with 100 randomisation runs in EstimateS (Colwell, 2009).

opencc-by-4.0Aug 2013View details →

Fig. 3. Activity patterns for 14 in Camera-Trapping Survey Of Mammals In And Around Imbak Canyon Conservation Area In Sabah, Malaysian Borneo

Fig. 3. Activity patterns for 14 mammal species (with n ≥ 8) photocaptured in and around Imbak Canyon Conservation Area in central Sabah, Malaysian Borneo. Dotted bar indicates percent frequency of independent photographs taken during the day time (0600–1800 hours); Black bar indicates percent frequency of independent photographs taken during night time (1800–0600 hours). Species are listed in order of decreasing frequency of diurnal activity. Numbers in parentheses indicate sample size.

opencc-by-4.0Aug 2013View details →

Fig. 1 in Camera-Trapping Survey Of Mammals In And Around Imbak Canyon Conservation Area In Sabah, Malaysian Borneo

Fig. 1. Imbak Canyon Conservation Area (ICCA) in central Sabah, northern part of Malaysian Borneo. Circles show the localities of 13 plots (P1–P13) where camera traps were placed (+). Each plot is approximately 3.5 km in radius.

opencc-by-4.0Dec 2021View details →

Fig. 1 in Blastocystis occurrence and subtype diversity in wild European terrestrial mammals - The case of Białowieza˙Primeval Forest (NE Poland)

Fig. 1. Study area with localization and number of Blastocystis-positive and Blastocystis-negative animals of particular mammalian species.

opencc-by-4.0Dec 2021View details →

Fig. 2 in Blastocystis occurrence and subtype diversity in wild European terrestrial mammals - The case of Białowieza˙Primeval Forest (NE Poland)

Fig. 2. Bayesian inference tree based on fragment of sequences obtained from the small subunit rRNA gene (SSU rDNA) of Blastocystis isolates of the present study, performed using MrBayes 3.2.7a. The Bayesian posterior probabilities are shown adjacent to branch nodes.

opencc-by-4.0Aug 2021View details →

Fig. 4 in Small mammals from the lasting fragments of Araucaria Forest in southern Brazil: a study about richness and diversity

Fig. 4. Dendrogram from the cluster analysis of the similarity of small mammals sampled at five vegetation types of Piraí do Sul National Forest, ParanÁ state, Brazil (PP, Pine Plantation; RF, Riparian Forest; AP, Araucaria Plantation; NR, Natural Regeneration forest; HA, High Altitude forest).