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Fig. 1 in Prevalence and geographic distribution of Babesia conradae and detection of Babesia vogeli in free-ranging California coyotes (Canis latrans)

Fig. 1. Base pair differences in a 70 base pair region of the 18S gene from Babesia conradae DNA sequences isolated from California coyotes (Canis latrans) splenic samples collected between 2015 and 2019 compared to published sequence available in GenBank.

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Fig. 2 in First detection and low prevalence of Pearsonema spp. in wild raccoons (Procyon lotor) from Central Europe

Fig. 2. Egg of Pearsonema spp. in urine sediment. The egg shows the characteristic features (barrel-shaped with bipolar plugs). Based on their morphology, the eggs were likely to be P. plica (see Discussion). Scale: 20 μm.

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Fig. 1 in First detection and low prevalence of Pearsonema spp. in wild raccoons (Procyon lotor) from Central Europe

Fig. 1. Sampling areas, sample size (n) and prevalence of Pearonema spp. in wild raccoons (Procyon lotor) from Luxembourg, Poland and Germany. Luxembourg: LUX Luxembourg; Poland: ZL administrative district of Zgorzelecki; Germany: NH Northern Harzvorland, Saxony-Anhalt and administrative district of BZ Bautzen, Saxony; EIC Eichsfeld, Thuringia; PR Prignitz, Brandenburg; GO¨G¨oppingen, Baden-Württemberg.

Fig. 1 in "Migratory beekeeping and its influence on the prevalence and dispersal of pathogens to managed and wild bees"

Fig. 1. Flow chart of the process of the systematic review on the different impacts of migratory beekeeping (MB), including the number of studies analysed at each step of the review process. Detailed data in Supplementary Table 1.

Fig. 2 in "Migratory beekeeping and its influence on the prevalence and dispersal of pathogens to managed and wild bees"

Fig. 2. Cumulative number of publications examining in general the impact of migratory beekeeping (blue dots) and in particular the prevalence of pathogens (orange dots) from 1990 to 2022. Exponential trend lines are represented by dashed lines. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 3 in Prevalence and new genotypes of Enterocytozoon bieneusi in wild rhesus macaque (Macaca mulatta) in China: A zoonotic concern

Fig. 3. Sequence variation in the ITS region of the rRNA gene of Enterocytozoon bieneusi isolates from rhesus macaque. The ITS sequences of 5 known genotypes (D, PL9, CAF4, EbpC, and SCC-2) and 8 novel genotypes (Mul6 to 13) identified in this study, were aligned with each other. The dots and transverse lines indicate base identities and deletions, respectively, relative to the ITS sequence of genotype D.

Fig. 2. Phylogenetic relationship among the Enterocytozoon bieneusi groups. The relationship between the E in Prevalence and new genotypes of Enterocytozoon bieneusi in wild rhesus macaque (Macaca mulatta) in China: A zoonotic concern

Fig. 2. Phylogenetic relationship among the Enterocytozoon bieneusi groups. The relationship between the E. bieneusi genotypes identified in this study and other known genotypes deposited in GenBank was inferred by neighbor-joining analysis of ITS sequences based on genetic distance using the Kimura-2-parameter model. The numbers on the branches represent percent bootstrapping values from 1000 replicates, with more than 50% shown in the tree. Each sequence is identified by its accession number, genotype designation, and host origin. Genotypes marked with black dot are identified in this study.

Fig. 3 in Prevalence of fish-borne zoonotic trematode infection in Jilin Province, China

Fig. 3. The phylogenetic tree of FZTs obtained in this study with other trematodes based on ITS sequences. ITS sequences of C. sinensis, M. orientalis and E. japonicus from fish were obtained and compared. They had the same similarity and were deposited into NCBI (No. MW828640, MW828729 and MW828605). The phylogenetic relationship between the FZTs obtained in this study and other trematodes based on ITS sequences was analyzed via MP, NJ and ML using A. chongqingens as the outgroup. The scale bar indicates an evolutionary distance of 0.10 substitutions per site in the sequence. The ITS sequences of C. sinensis, M. orientalis and E. japonicus obtained in this study (marked with *) was 100% consistent with the sequences of C. sinensis (MF319654), M. orientalis (MK482055) and E. japonicus (KT873314) deposited in NCBI GenBank.

Fig. 5 in Prevalence of fish-borne zoonotic trematode infection in Jilin Province, China

Fig. 5. The prevalence of FZTs in different months in wild freshwater fish in Jilin Province, China. The prevalence of FZTs in freshwater fish gradually increased and then decreased, with the highest prevalence of C. sinensis and E. japonicus in August and the highest prevalence of M. orientalis in September. *p <0.05 was considered to be a significant difference, and the prevalence in November was used as a control. The significances of C. sinensis, M. orientalis and E. japonicus in different months are marked in red *, green * and blue *, respectively. (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 Prevalence and genetic diversity of Enterocytozoon bieneusi in nonhuman primates in Northern and Central China

Fig. 1. Phylogenetic tree of E. bieneusi genotypes identified in this study and known genotypes based on the Neighbor-Joining analysis of the internal transcribed spacer of the rRNA gene. The numbers on the branches represent percent bootstrapping values from 500 replicates, with values of>70.0% shown in the tree. The genotypes identified in this study were marked, with △ for known genotypes and ▴ for the novel genotypes.

Fig. 2 in Prevalence of fish-borne zoonotic trematode infection in Jilin Province, China

Fig. 2. The metacercariae and eggs of C. sinensis, M. orientalis and E. japonicus.C. sinensis metacercariae encysted on the flesh of P. parva, scale bar = 50 μm (A). M. orientalis metacercariae encysted on the flesh of P. parva, scale bar = 50 μm (B). E. japonicus metacercariae encysted on the gills of R. sinensis, scale bar = 50 μm (C). C. sinensis metacercariae isolated from P. parva, scale bar = 50 μm (D). M. orientalis metacercariae isolated from P. parva, scale bar = 50 μm (E); E. japonicus metacercariae isolated from R. sinensis, scale bar = 50 μm (F). C. sinensis egg in feces of canine, scale bar = 10 μm (G). M. orientalis egg in feces of duck, scale bar = 10 μm (H). E. japonicus eggs in feces of canine and duck, scale bar = 10 μm (I, J). EC, excretion cyst; ET, excretion tube; EO, egg operculum; IW, inner cyst wall; OW, outer cyst wall; ME, metacercariae; MI, miracidium; SP, shoulder peaks; SE, small spine at the rear end; OS, oral sucker; VS, ventral sucker.

Fig. 2 in High Toxocara cati prevalence in wild, free-ranging Eurasian lynx (Lynx lynx) in Finland, 1999-2015

Fig. 2. The estimated Eurasian lynx (Lynx lynx) population size and Toxocara cati prevalence (%, 95% confidence interval) in Finland, by year.

Fig. 3 in High Toxocara cati prevalence in wild, free-ranging Eurasian lynx (Lynx lynx) in Finland, 1999-2015

Fig. 3. Number of Toxocara cati worms in Eurasian lynx (Lynx lynx) in Finland, by age and sex. Median, first and third quartiles, and minimum and maximum are shown.

Fig. 1 in High Toxocara cati prevalence in wild, free-ranging Eurasian lynx (Lynx lynx) in Finland, 1999-2015

Fig. 1. The head, the cephalic alae and the body of the Toxocara cati found from female Eurasian lynx (Lynx lynx) from Finland. The measurement scale has red marks at 1 mm intervals. (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 Sero-prevalence and risk factors of Toxoplasma gondii infection in wild cervids in Denmark

Fig. 1. The geographical distribution of wild cervids included in the study and the number of animals tested positive for antibodies against Toxoplasma gondii in the hunting season 2017–2018 in Denmark (n = 428). Shown by region and proportion of species sampled (roe deer, fallow deer or red deer) in each region. Pie charts indicate proportion of samples from each cervid species. Note Sika deer was only sampled in Mid-Jutland (n = 14), and hence not included in the map. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 3 in Effect of urbanization on zoonotic gastrointestinal parasite prevalence in endemic toque macaque (Macaca sinica) from different climatic zones in Sri Lanka

Fig. 3. GI parasite genera types identified from fecal samples of toque macaques. I. Protozoan types: (A) Balantidium cyst, (B) Balantidium trophozoite, (C) Endolimax cyst, (D) Entamoeba cyst, (E) Isospora cyst. (F) Unidentified protozoan cyst; II. Cestode types: (G) Bertiella ova, (H) Diphyllobothrium ova, (I) Hymenolepis ova; III. Trematode types: (J–K) Unidentified trematode ova; IV. Acanthocephalan type: (L) Moniliformis ova; V. Nematode types: (M) Oesophagostomum ova, (N) Strongyloides ova, (O) Ascaris ova, (P) Trichuris ova, (Q) Strongyle/ Hookworm ova, (R) Enterobius ova, (S)Trichostrongylus ova, (T) Unidentified nematode ova.

Fig. 2 in Effect of urbanization on zoonotic gastrointestinal parasite prevalence in endemic toque macaque (Macaca sinica) from different climatic zones in Sri Lanka

Fig. 2. Map of Sri Lanka with sampling localities in the dry and the wet zones and the montane region.

Fig. 4 in Effect of urbanization on zoonotic gastrointestinal parasite prevalence in endemic toque macaque (Macaca sinica) from different climatic zones in Sri Lanka

Fig. 4. Number of parasite genera types (species richness) infecting M. s. aurifrons, M. s. sinica and M. s. opisthomelas in urban, suburban, and wild habitats.

Fig. 1 in Effect of urbanization on zoonotic gastrointestinal parasite prevalence in endemic toque macaque (Macaca sinica) from different climatic zones in Sri Lanka

Fig. 1. The three subspecies of macaque's endemic to Sri Lanka. (A) Common macaque (Macaca sinica sinica), (B) dusky or pale-fronted macaque (M. s. aurifrons), and (C) hill-zone macaque (M. s. opisthomelas) (image courtesy: Madura De Silva).