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Figure 4 in Genotoxic effects of oxyclozanide on hemocytes of Galleria mellonella (Lepidoptera: Pyralidae) larvae

Figure 4. Tail moment in hemocytes of seventh instar larvae of G. mellonella. Bars represent the means (± SE) of four replicates. Means followed by different letters are significantly different from each other, p <0.05 (LSD Test).

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Figure 3 in Genotoxic effects of oxyclozanide on hemocytes of Galleria mellonella (Lepidoptera: Pyralidae) larvae

Figure 3. Tail DNA% in hemocytes of seventh instar larvae of G. mellonella. Bars represent the means (± SE) of four replicates. Means followed by different letters are significantly different from each other, p <0.05 (LSD Test).

opencc-by-4.0Jan 2023View details →

Figure 1 in Lethal and sublethal effects of exposure to Roundup 360 Plus for the Chaoborus flavicans larvae (Diptera: Chaoboridae)

Figure 1. The distribution of C. flavicans larvae within the water column under different concentrations of GLY. Box-mean, whisker-SD, n = 10, 0-close to the bottom, 1-in the water column, 2-close to the surface of the water. The letters above boxes indicate significant differences between time points (Tukey test, p <0.05)

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Figure 2 in Lethal and sublethal effects of exposure to Roundup 360 Plus for the Chaoborus flavicans larvae (Diptera: Chaoboridae)

Figure 2. Morphological malformations of C. flavicans larvae. a– control organisms. Note two pairs of air sacs (arrows) and the digestive system (arrowhead). b– magnified picture of a pair of air sacs of a control insect. Note the regular distribution of chromatophores over the sacs. c– C. flavicans larva exposed to 20 µg/L GLY. Note altered pigmentation of the air sacs (arrow) and contortion of the body. d– C. flavicans larva exposed to 100 µg/L GLY. Note altered pigmentation, a contortion of the body that is close to the front air sacs (arrowhead), and darkening of the body. e, f– C. flavicans larva exposed to 400 µg/L GLY. Note the disappearance of pigmentation of air sacs, and the darkening of the body.

Fig. 1 in Nematode larva migrans caused by Toxocara cati in the North Island brown kiwi (Apteryx mantelli)

Fig. 1. Histology. (A) Typical inflammatory granuloma in the lung of a kiwi, containing several oblique nematode larval sections (H&E, bar = 50 μm). (B) Crosssection of a nematode larva within an inflammatory granuloma in the brain of a kiwi, showing bilateral alae (H&E, bar = 20 μm).

Fig. 2 in Patterns of parasite eggs, oocysts and larvae shedding by moose in the Biebrza marshland (NE Poland)

Fig. 2. The relationship between the EPG of Trichostrongylidae family members, Moniezia spp., Parafasciolopsis fasciolaemorpha, the LPG of Elaphostrongylus sp. and mean monthly temperature (red continuous line). Blue continuous line shows the median EPG/LPG and broken lines indicate its 95% confidence interval. (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 Patterns of parasite eggs, oocysts and larvae shedding by moose in the Biebrza marshland (NE Poland)

Fig. 1. The relationship between the prevalence of Nematodirella alcidis and Moniezia spp. eggs and mean monthly temperature (red continuous line). Blue continuous line shows the prevalence and broken lines indicate its 95% confidence interval. (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 Patterns of parasite eggs, oocysts and larvae shedding by moose in the Biebrza marshland (NE Poland)

Fig. 3. The relationship between the median EPG of Parafasciolopsis fasciolaemorpha, the median LPG of Elaphostrongylus sp. and the presence of snow cover.

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Fig. 1 in First detailed records of water mite larvae (Hydrachnidia: Hydrovolzidae, Hydryphantidae) parasitizing empidid flies (Diptera: Empididae: Clinocerinae)

Fig. 1. Types of habitat where infested and uninfested clinocerine species were found; a – the Mała Łąka Valley, June 2017; b – the same locality, October 2017; c – the Kościeliska Valley, May 2018; d – the same locality, November 2018; e – Białka River, Łysa Polana, August 2017; f – Cracow Gorge, June 2017 (photographs by I. Słowińska).

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Figure 1 in Identity of planidium larvae (Hymenoptera: Chalcidoidea) previously recorded on Antillean scorpions

Figure 1: Ventral aspect of the planidium found on Centruroides anchorellus (Scorpiones: Buthidae) (after Armas, 2003, fig. 1).

Fig. 3 in Effects of dietary intake of volcanic ash from Puyehue Cordon Caulle on Tenebrio molitor (Coleoptera: Tenebrionidae) larvae under laboratory conditions

Fig. 3. Mean body weight of larvae (mg) fed 30,000 and 50,000 ppm of volcanic ash treated flour disks afer 15 d. Bars with the same letter are not significantly different α = 0.05. Bioassay endpoint = 15 d, n = 10, substrate = treated and control insect food (ANOVA: F = 93.67; df = 2; P <0.0001).

Fig. 1 in Effects of dietary intake of volcanic ash from Puyehue Cordon Caulle on Tenebrio molitor (Coleoptera: Tenebrionidae) larvae under laboratory conditions

Fig. 1. Chemical composition of ash from Puyehue Cordon Caulle eruption collected in Collón Curá, Neuquén, Argentina (40.0400°S, 70.2405°W) 15 Jun 2011, determined by energy dispersive spectroscopy. Previously published in Buteler et al. (2011), Revista de la Sociedad Entomológica Argentina 70 (3–4), Figure 3, copyright RSEA, reproduced with permission.

Fig. 6 in Effects of dietary intake of volcanic ash from Puyehue Cordon Caulle on Tenebrio molitor (Coleoptera: Tenebrionidae) larvae under laboratory conditions

Fig. 6. Molting rate of Tenebrio molitor larvae feed on flour disks treated with sub-lethal concentrations (500, 1,000, 5,000 ppm) of volcanic ash. Molting rate = number of molts per incubation period of 27 d.

Fig. 5 in Effects of dietary intake of volcanic ash from Puyehue Cordon Caulle on Tenebrio molitor (Coleoptera: Tenebrionidae) larvae under laboratory conditions

Fig. 5. Larval body length (cm) of Tenebrio molitor larvae fed on flour disks treated with sub-lethal concentrations (500, 1,000, 5,000 ppm) of volcanic ash. Bars with the same letter are not significantly different α = 0.05. Bioassay endpoint = 27 d, n = 10, substrate = treated and control insect food (ANOVA: F = 95.15; df = 3; P <0.0001).

Fig. 4 in Effects of dietary intake of volcanic ash from Puyehue Cordon Caulle on Tenebrio molitor (Coleoptera: Tenebrionidae) larvae under laboratory conditions

Fig. 4. Mean body weight of larvae (mg) fed on sub lethal concentrations (500, 1,000, 5,000 ppm) of volcanic ash treated flour disks. Bars with the same letter are not significantly different at α = 0.05. Bioassay endpoint = 27 d, n = 10, substrate = treated and control insect food (ANOVA: F = 133.97; df = 3; P <0.0001).

Fig. 5. Average and 95 in Larvae occurrences of Rhamdia quelen (Quoy & Gaimard, 1824) (Siluriformes: Heptapteridae) in an area under dam influence in the upper Paraná River region, Brazil

Fig. 5. Average and 95% confidence interval for the mean log (Dens. + 1) observed in the different sampling stations 10 during the period (Different letters indicate significant differences according to the Unequal HSD test).

Fig. 4 in Larvae occurrences of Rhamdia quelen (Quoy & Gaimard, 1824) (Siluriformes: Heptapteridae) in an area under dam influence in the upper Paraná River region, Brazil

Fig. 4. Monthly average values of environmental variables in different spawning periods in Ilha Grande National Park.

Fig. 2 in Larvae occurrences of Rhamdia quelen (Quoy & Gaimard, 1824) (Siluriformes: Heptapteridae) in an area under dam influence in the upper Paraná River region, Brazil

Fig. 2. Average abundance of R. quelen larvae by spawning period (a), month (b), and sampling station (c).

Fig. 3 in Larvae occurrences of Rhamdia quelen (Quoy & Gaimard, 1824) (Siluriformes: Heptapteridae) in an area under dam influence in the upper Paraná River region, Brazil

Fig. 3. Monthly density and per sampling stations of the larval development stages of Rhamdia quelen in Ilha Grande National Park.

Fig. 1 in Larvae occurrences of Rhamdia quelen (Quoy & Gaimard, 1824) (Siluriformes: Heptapteridae) in an area under dam influence in the upper Paraná River region, Brazil

Fig. 1. Location of sampling stations (black dots). (1: Bandeirantes right channel; 2: Amambaí; 3: Triângulo; 4: Porto Santo Antônio; 5: Peruzzi; 6: Paraná/Iguatemi; 7: Iguatemi; 8: Paraná/Saraiva; 9: Saraiva middle; 10: Saraiva channel; 11: Ilha Grande right channel; 12: Bandeirantes left channel; 13: Ilha Grande Pontal; 14: Alvarenga; 15: Esmeralda; 16: Três Coqueiros; 17: São João; 18: Porto Luiz; 19 Porto Cerâmica; 20: Piquiri; 21: Porto Terra Roxa; 22: Ilha Grande left channel).