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262 results for “trematodes”
Fig. 1 in Tegumental topography and molecular characterisation of two trematodes (Platyhelminthes: Digenea) from Clarias gariepinus (Burchell, 1822) in Kenya
Fig. 1. Geographical location of the study area: A– Kenya shaded on the African continent; B – shows position of Nyandarua County in Kenya; C – indicates the position of the Lake Ol'Bolossat and the sampling sites (S1–S3).
Fig. 4 in Tegumental topography and molecular characterisation of two trematodes (Platyhelminthes: Digenea) from Clarias gariepinus (Burchell, 1822) in Kenya
Fig. 4. Scanning electron micrographs of Tylodelphys mashonensis. (A) ventral surface ultrastructure, (B) sensory papillae surrounding the oral sucker (C) ventral sucker surrounded by small and large papillae, (D) well organized holdfast organ with spines (abbreviations: ps-pseudo suckers, os-oral sucker, ho- holdfast organ, vs-ventral sucker, pp-papillae, sp-symmetrical papillae, lp- large papillae, hf-holdfast fissure).
Fig. 4 in Spatio-temporal variation in prevalence and intensity of trematodes responsible for waterfowl die-offs in faucet snail-infested waterbodies of Minnesota, USA
Fig. 4. Models of Cyathocotyle bushiensis (Cb) and Sphaeridiotrema spp. (Sg) metacercarial prevalence (prev) and intensity (int) in the waterbodies we studied in northern Minnesota during 2011‾2013; a) East Winnibigoshish index area, b) West Winnibigoshish index area, c) Lower Twin Lake, d) Crow Wing River, e) White Earth ponds, f) Shell River. Depth_cm is water depth at the sampling location. Dist.scaup is the minimum Euclidean distance between a given waypoint and the nearest point sampled under a raft of scaup in either the same season, or up to two seasons prior in that same year. Log.abund is the log transformed snail abundance at a sampling point. Size.mean is the mean snail size at a sampling point. Year2012 and Year2013 are comparisons between samples collected in 2011 vs 2012 and 2011 vs 2013, respectively.
Fig. 3 in Spatio-temporal variation in prevalence and intensity of trematodes responsible for waterfowl die-offs in faucet snail-infested waterbodies of Minnesota, USA
Fig. 3. Average intensity of (a) Cyathocotyle bushiensis (Cb) and (b) Sphaeridiotrema spp. (Sg) metacercariae in each of the waterbodies studied in northcentral Minnesota during nine seasons in 2011‾2013 with 95% confidence intervals. Note that waterbody specific y-axis scales are used to highlight differences within a waterbody.
Fig. 2 in Spatio-temporal variation in prevalence and intensity of trematodes responsible for waterfowl die-offs in faucet snail-infested waterbodies of Minnesota, USA
Fig. 2. Average prevalence of (a) Cyathocotyle bushiensis (Cb) and (b) Sphaeridiotrema spp. (Sg) metacercariae in each of the waterbodies studied in northcentral Minnesota during nine seasons in 2011‾2013 with 95% confidence intervals.
Fig. 1 in Spatio-temporal variation in prevalence and intensity of trematodes responsible for waterfowl die-offs in faucet snail-infested waterbodies of Minnesota, USA
Fig. 1. Map of study area in northcentral Minnesota depicting the study lakes with county boundaries, within the state and USA.
Рис. 8. ОтноситеΛьная преΑставΛенность транскриптов патогенраспознающих рецепторов в гемоцитах моΛΛюсков Planorbarius corneus, заражённых трематоΑами Bilharziella polonica (I) и незаражённых особей (N) Fig. 8. Relative number of transcripts of pattern recognition receptors from hemocytes of Planorbarius corneus molluscs infected with Bilharziella polonica trematodes (I) and uninfected individuals (N) in Pathogen recognition molecules from hemocytes of Planorbarius corneus molluscs (Planorbidae, Pulmonata)
Рис. 8. ОтноситеΛьная преΑставΛенность транскриптов патогенраспознающих рецепторов в гемоцитах моΛΛюсков Planorbarius corneus, заражённых трематоΑами Bilharziella polonica (I) и незаражённых особей (N) Fig. 8. Relative number of transcripts of pattern recognition receptors from hemocytes of Planorbarius corneus molluscs infected with Bilharziella polonica trematodes (I) and uninfected individuals (N)
Рис. 1. Станции сбора материаΛа по трематоΑам рыб в Мингечевирском воΑохраниΛище, 2016–2022 гг Fig. 1. Stations for collecting material on fish trematodes in the Mingachevir reservoir, 2016– 2022 in Ecological and faunistic analysis fish trematodes of the Mingechevir Reservoir
Рис. 1. Станции сбора материаΛа по трематоΑам рыб в Мингечевирском воΑохраниΛище, 2016–2022 гг Fig. 1. Stations for collecting material on fish trematodes in the Mingachevir reservoir, 2016– 2022
Fig. 7 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 7. Bayesian inference (BI) phylogram based on the partial (D1–D3 domains) sequences of 28S rDNA for the Opisthorchioidea. Posterior probability values are given above the branches. Support values with <0.95 posterior probability are omitted. The branch length scale-bar indicates the expected number of substitutions per site. The newly-generated sequences are highlighted in bold. Species of Ascocotyle are indicated in blue and the respective clade is demarcated with yellow rectangular. Doted rectangular outline the members of the family Heterophyidae. Outgroup taxa are represented in grey colour. The respective definitive hosts are symbol indicated on the tree. Abbreviations: Ad, Adult; MTC, metacercaria. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 5 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 5. Ascocotyle (Ascocotyle) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012'. Adults from the intestine of Spheniscus magellanicus (A and B) and metacercariae from the heart of Odontesthes argentinensis, Patagonia, Argentina. (C–E). (A) Total, ventral view, voucher (MLP-He 7503). (B) Anterior end with circumoral spines, voucher (IPCAS D-786). (C) Total, ventral view. (D) Middle part of body with ventrogenital complex, ventral view. (E) Anterior end with circumoral spines.
Fig. 4 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 4. Ascocotyle (Phagicola) cameliae n. sp. from the intestine Spheniscus magellanicus collected in Patagonia, Argentina. Scanning electron micrographs. (A) Detail of circumoral spines; note absence of tegumental spines. (B). Detail of papillae in region devoid of tegumental spines. (C and D) Detail of the mouth of the ventrogenital sac; note gonotyl in (D). (E) Posterior end, ventral view; note simple tegumental spines reaching up to the posterior extremity. (F) Pectinate (with 4–5 digit-like processes – teeth) tegumental spines on the anterior part of the body. (G) Pectinate (with 2–3 digit-like processes) tegumental spines on the middle part of the body. (H) Simple or 2- toothed tegumental spines on the posterior part of the body.
Fig. 3 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 3. Ascocotyle (Phagicola) cameliae n. sp. from the intestine of Spheniscus magellanicus collected in Patagonia, Argentina. (A–D) Anterior end with circumoral spines; note variation in spine number, 22 spines (A and B), 19 spines (C) and 24 spines (D). (E) Terminal genitalia, ventral view of paratype (IPCAS D-805).
Fig. 1 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 1. Ascocotyle (Phagicola) cameliae n. sp. from the intestine of Spheniscus magellanicus collected in Patagonia, Argentina. (A) Total, ventral view of holotype (MLPHe 7501). (B) Total, dorsal view of paratype (IPCAS D-805).
Fig. 2 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 2. Ascocotyle (Phagicola) cameliae n. sp. from the intestine Spheniscus magellanicus collected in Patagonia, Argentina. Scanning electron micrographs. (A and B) Total, ventral view. (C and D). Anterior end, apical view. (E). Anterior end, ventral view.
Fig. 6 in Heterophyid trematodes (Digenea) from penguins: A new species of Ascocotyle Looss, 1899, first description of metacercaria of Ascocotyle (A.) patagoniensis Hernández-Orts, Montero, Crespo, García, Raga and Aznar, 2012, and first molecular data
Fig. 6. Bayesian inference (BI) phylogram based on the partial (D1–D3 domains) sequences of 28S rDNA for the species of Ascocotyle. Posterior probability values are given above the branches. Support values with <0.95 posterior probability are omitted. The branch length scale-bar indicates the expected number of substitutions per site. The newly-generated sequences are colour indicated (in blue) and highlighted in bold. The outgroup is represented in grey colour. Host origins of the specimens sequenced are symbol indicated on the tree. (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 Air sac trematodes: Morishitium polonicum as a newly identified cause of death in the common blackbird (Turdus merula)
Fig. 1. Necropsy of Turdus merula, female. Gross lesions are represented by heavy parasite colonization of coelomic cavity. A. Many trematodes are clearly seen on different serosal membranes. Note the presence of parasites on the liver serosa, air sacs and pericardium (arrow). B. After removal of all the organs of the gastroenteric apparatus, an involvement of kidney and lungs serosa is also evident. Note the presence of an inflammatory focus with exudate at the periphery of the left lung (arrowhead).
Fig. 4 in Air sac trematodes: Morishitium polonicum as a newly identified cause of death in the common blackbird (Turdus merula)
Fig. 4. Maximum likelihood analyses of sequences of mitochondrial DNA loci of the newly isolated Morishitium polonicum and previously sequenced Cyclocoelidae. (A) CO1, (B) ND1. The bars indicate the number of substitutions per nucleotide.
Fig. 1 in Environmental and ecological factors driving trematode parasite community assembly in central Alberta lakes
Fig. 1. Host-Parasite diversity correlations. Spearman rank correlations of A) snail and trematode richness, pooled by site, B) non-pooled, sample-based, snail and trematode richness, C) snail and trematode effective species based on Shannon index (exp(H)) for all lakes, and D) effective species by each site at Buffalo Lake. PP = Pelican Point, RS = Rochon Sands, TN = The Narrows.
Fig. 3 in Environmental and ecological factors driving trematode parasite community assembly in central Alberta lakes
Fig. 3. Canonical correspondence analysis (CCA) of trematode component communities. Relative abundances of trematode species by sample are constrained by environmental variables from the best-fit model (community \lake trophic status \+ ecoregion \+ latitude). Trematode species abbreviations are shown in grey. CCA results are in red as eigenvectors. Ecoregions are identified with a blue dotted line. The trophic status of each lake is identified with an ellipse.
Fig. 2 in Environmental and ecological factors driving trematode parasite community assembly in central Alberta lakes
Fig. 2. Multivariate Homogeneity of Group Dispersion for Trematode Communities. Bray-Curtis dissimilarities were used to examine the homogeneity of variance among samples (trematode species counts) when grouped by different geographical or anthropogenic-use distinctions. The left panels show the twodimensional visualizations of the data by Principal Coordinate Analysis (PCA) plots. Each grouping is labeled in the center, and ellipses represent 95% confidence intervals. The right panels provide a boxplot of the distance to centroid for each group in the multivariate analysis. A) samples grouped by site, B) grouped by river basin, C) grouped by ecoregion, D) group by site-type or anthropogenic use (beach or boat launch). Statistical significance for differences between groups is indicated by an asterisk.
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