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Fig. 12 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 12. Corrected number of observations per two-month period for Trichoniscoides albidus (N = 97).

Fig. 10 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 10. Corrected number of observations per two-month period for Metatrichoniscoides leydigii (N = 16).

Fig. 11. a in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 11. a, Ligidium hypnorum; b, Androniscus dentiger; c, Haplophthalmus mengii; d, Hyloniscus riparius; e, Metatrichoniscoides leydigii; f, Trichoniscoides albidus; g, Trichoniscoides helveticus; h, Trichoniscus provisorius.

Fig. 8 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 8. Corrected number of observations per two-month period for Haplophthalmus montivagus (N = 157).

Fig. 24 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 24. Corrected number of observations per two-month period for Platyarthrus hoffmannseggii (N = 163).

Fig. 1 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 1. Different habitats in Belgium well suited for terrestrial isopods. a, old forest in Parike, Belgium; b, disused quarry in Reuland, Belgium; c, stream side (dyke) of the Dyle river in Rijmenam, Belgium; d, old cemetery in Rahier, Belgium; e, old stable in a meadow near Saint-Saveur, Belgium.

Fig. 2. a in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 2. a, Ligia oceanica; b, Haplophthalmus danicus; c, Miktoniscus patience; d, Trichoniscus pygmaeus; e, Armadillidium pictum; f, Armadillidium vulgare; g, Porcellio dilatatus; h, Porcellio laevis.

Figure 4 in Antimicrobial activity of noni fruit essential oil on Escherichia coli O157:H7 and Salmonella Enteritidis

Figure 4. The GC chromatogram of noni EO: 1. α-pinene; 2. camphene; 3. Methyl ester; 4. 2- heptanone; 5. Caprylic acid.

Figure 1 in Antimicrobial activity of noni fruit essential oil on Escherichia coli O157:H7 and Salmonella Enteritidis

Figure 1. The effect of noni EO on E. coli O157:H7 and S. Enteritidis using the direct spreading- plate method on the MIC value of noni EO towards both pathogens.

Figure 3 in Antimicrobial activity of noni fruit essential oil on Escherichia coli O157:H7 and Salmonella Enteritidis

Figure 3. The survival of E. coli O157:H7 and S. Enteritidis as affected by noni EO in TBS after a treatment for 16 hours.

Figure 2 in Antimicrobial activity of noni fruit essential oil on Escherichia coli O157:H7 and Salmonella Enteritidis

Figure 2. The effect of noni EO on E. coli O157:H7 and S. Enteritidis using the broth dilution method in TBS to determine the MBC value of noni EO against both pathogens.

Fig. 2 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans

Fig. 2. The efficacy of the natural components against E. tenella sporozoites. The viability of sporozoites was determined at various concentrations of the compounds that showed effectiveness at 100 μM. The half maximal inhibitory concentration (IC50) value was determined from the approximate curves obtained from these results. SPZ: sporozoite.

Fig. 1 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans

Fig. 1. Direct effects of the natural components derived from alpine plants on E. tenella sporozoites. The viability of sporozoites treated with each natural component derived from alpine plants or lasalocid (positive control) with the viability of the DMSO-treated group set as 100%. The final concentration was 100 μM for the natural components, and 1 μM for lasalocid. SPZ: sporozoite; Las: lasalocid. Outliers were tested using Thompson's test (p <0.05), and the student's t-test was utilized to compare the data with the DMSO-treated group as a control (**p <0.01, ***p <0.001, ****p <0.0001).

Fig. 3 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans

Fig. 3. Confirmation of the active compounds using commercially available compounds and their efficacy. (A) The viability of sporozoites treated with each commercially available compound or lasalocid (positive control) was compared to the viability of the DMSO-treated group, which was set as 100%. The final concentration was 100 μM for the synthetic compounds, and 1 μM for lasalocid. SPZ: sporozoite, Las: lasalocid. The student's t-test was used for the comparisons (****p <0.0001) without outliers, as tested using Thompson's test (p <0.05). (B) The viability of sporozoites was determined at each concentration of the synthetic compounds that showed effectiveness at 100 μM. The half maximal inhibitory concentration (IC50) value was determined by approximating the curves obtained from the results.

Fig. 4 in Anticoccidial activity of the secondary metabolites in alpine plants frequently ingested by wild Japanese rock ptarmigans

Fig. 4. The inhibitory effects of the natural components derived from alpine plants on sporozoite cell invasion. The invasion rate of sporozoites treated with each natural component derived from alpine plants or lasalocid (positive control) with the viability of the DMSO-treated group set as 100%. Each compound was used at its maximum non-toxic concentration. Las: lasalocid. The student's t-test was utilized to compare the data with the DMSO-treated group as a control (**p <0.01, ***p <0.001, ****p <0.0001). Outliers were identified and removed using Thompson's test (p <0.05).

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Neutron activation analysis data of pottery from Cerro Mayal and the Chicama Valley, Peru

<p>Neutron activation analysis data of pottery from Cerro Mayal and other sites in the Chicama Valley, La Libertad Department, Peru.</p>

Fig. 5 in Influence of seasonality and biological activity on infection by helminths in Cantabrian bear

Fig. 5. Seasonal kinetics of helminths egg-output in Cantabrian brown bears (n = 248) according to their activity periods. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 2 in Influence of seasonality and biological activity on infection by helminths in Cantabrian bear

Fig. 2. Seasonal variations in the prevalence of helminth infection in feces of brown bears (n = 248) from the western part of the Cantabrian Mountains (Asturias and Le´on provinces, Spain). (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)

Fig. 4 in Influence of seasonality and biological activity on infection by helminths in Cantabrian bear

Fig. 4. Seasonal variations in the prevalence of helminth infection in feces of brown bears (n = 248) from Cantabrian Mountains (Spain) according to their activity periods. (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 Influence of seasonality and biological activity on infection by helminths in Cantabrian bear

Fig. 1. Distribution of the sampling of brown bear feces (n = 248) in the western part of the Cantabrian Mountains (Asturias and Le´on provinces, Spain). (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)