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Figure 2 in Infestation and effect of parasitic isopod Epipenaeon ingens ingens Nobili, 1906 on commercial shrimp species in the eastern Mediterranean: a case study of the population of brown shrimp Penaeus aztecus Ives, 1891

Figure 2. Percentage of infected and uninfected shrimps by carapace length (CL) and by sex of P. aztecus sampled in Antalya Bay (red circular: an observed percentage of the infection, thick line: correlation line).

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Figure 6 in Infestation and effect of parasitic isopod Epipenaeon ingens ingens Nobili, 1906 on commercial shrimp species in the eastern Mediterranean: a case study of the population of brown shrimp Penaeus aztecus Ives, 1891

Figure 6. Box and Whisker plot representation of the negative effect of E. ingens ingens on the gonadal development of the female host shrimp P. aztecus.

Figure 6 in Determining some biological parameters of Aenasius arizonensis (Girault) (Hymenoptera: Encyrtidae) on cotton mealybug and the rate of parasitism in field conditions

Figure 6. Parasitism rate of Aenasius arizonensis with Daily mean temperature and mean R.H.in 2018 for Balcalı /Adana.

Figure 4 in Determining some biological parameters of Aenasius arizonensis (Girault) (Hymenoptera: Encyrtidae) on cotton mealybug and the rate of parasitism in field conditions

Figure 4. Age-specific survival rate (l), age-specific fecundity (m), and age-specific maternity (lxm) of X x x Aenasius arizonensis.

Weekly mean parasitism rate (%) Daily mean Temperature (°C) Daily Mean R.H. (%) Figure 7. Parasitism rate of Aenasius arizonensis with Daily mean temperature and mean R.H.in 2018 for Tömük / Mersin. in Determining some biological parameters of Aenasius arizonensis (Girault) (Hymenoptera: Encyrtidae) on cotton mealybug and the rate of parasitism in field conditions

Weekly mean parasitism rate (%) Daily mean Temperature (°C) Daily Mean R.H. (%) Figure 7. Parasitism rate of Aenasius arizonensis with Daily mean temperature and mean R.H.in 2018 for Tömük / Mersin.

Figure 1. a in Determining some biological parameters of Aenasius arizonensis (Girault) (Hymenoptera: Encyrtidae) on cotton mealybug and the rate of parasitism in field conditions

Figure 1. a) Parasitized Phenacoccus solenopsis individuals on cotton leaves (Adult female), b) Phenacoccus solenopsis individuals on cotton during laboratory studies (adult female).

Figure 3 in Determining some biological parameters of Aenasius arizonensis (Girault) (Hymenoptera: Encyrtidae) on cotton mealybug and the rate of parasitism in field conditions

Figure 3. The longevity of immature and mature stages of A.arizonensis.Y axis represents age-stage specific survival rate (S xj), X axis indicates the age of parasitoid.

opencc-by-4.0Dec 2004View details →

Fig. 3 in First Record Of The Parasitic Barnacle Sacculina Scabra Boschma, 1931 (Crustacea: Cirripedia: Rhizocephala) Infecting The Shallow Water Swimming Crab Charybdis Truncata

Fig. 3. Colleteric gland tubules of Sacculina scabra on the A) left hand side and B) right hand side of the visceral mass. Scale bar in m.

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Fig. 2 in First Record Of The Parasitic Barnacle Sacculina Scabra Boschma, 1931 (Crustacea: Cirripedia: Rhizocephala) Infecting The Shallow Water Swimming Crab Charybdis Truncata

Fig. 2. Transverse sections of A) male receptacles, B) receptacle duct near the male receptacles showing the thick lining, C) folded lining (f) of receptacle duct, D) the paired receptacle ducts joined in the same chamber, E) the receptacle duct separated again at the region of the duct opening, F) receptacle duct opening, showing thick, cuticular lining. All the figures are to the same scale. Scale bar in m.

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Fig. 1 in First Record Of The Parasitic Barnacle Sacculina Scabra Boschma, 1931 (Crustacea: Cirripedia: Rhizocephala) Infecting The Shallow Water Swimming Crab Charybdis Truncata

Fig. 1. Drawing of the externa of Sacculina scabra from a male and female Charybdis truncata. Scale bar in mm.

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 Detection of haemosporidian parasites in wild and domestic birds in northern and central provinces of Iran: Introduction of new lineages and hosts

Fig. 3. Median joining haplotype network of Haemoproteus lineages. Detected sequences in this study are in bold.

Fig. 2. Bayesian tree reconstructed using 478 in Detection of haemosporidian parasites in wild and domestic birds in northern and central provinces of Iran: Introduction of new lineages and hosts

Fig. 2. Bayesian tree reconstructed using 478-bp mitochondrial cytb gene for avian blood parasites lineages. The amplified sequences in the current study are highlighted in bold. Posterior probability support of>0.8 is displayed for each branch. Schematic tree is summarized in section A and separated clade for each genus is given in sections of B (Plasmodium), C (Haemoproteus), and D (Leucocytozoon).

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.

Fig. 1 in Diversity of helminth parasites of eight siluriform fishes from the Aguapeí River, upper Paraná basin, São Paulo state, Brazil

Fig. 1. Map of the study area. Black dots represent the sampling location in the mouth of the Aguapeí River, Upper Paraná River basin, at the border of São Paulo and Mato Grosso do Sul States, Brazil.

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.

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.

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Fig. 2 in Rainfall as a driver of seasonality in parasitism

Fig. 2. Relationship between rainfall measured two months prior to parasitological sampling (Rt-2) and the probability of Trichuris egg presence. Points (triangles = territorial males, circles = bachelor males) and the line (with 95% confidence intervals) are predicted values from a binomial generalized linear mixed model.

Fig. 2. a in Not playing by the rules: Unusual patterns in the epidemiology of parasites in a natural population of feral horses (Equus caballus) on Sable Island, Canada

Fig. 2. a) Dictyocaulus arnfieldi first-stage larvae showing typical granular appearance and beginning of cuticular separation b) closer view of tail showing stylet, or spear.